ML20066F948
ML20066F948 | |
Person / Time | |
---|---|
Site: | San Onofre |
Issue date: | 11/15/1982 |
From: | SOUTHERN CALIFORNIA EDISON CO. |
To: | |
Shared Package | |
ML13323A342 | List: |
References | |
PROC-821115, NUDOCS 8211190240 | |
Download: ML20066F948 (78) | |
Text
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OFFSITE DOSE CALCULATION MANUAL SAN ONOFRE NUCLEAR GENERATING STATION UNITS 2&3 i
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8211190240 8211 to DR ADOCK 05000361 PDR m
. , o ODCM TABLE OF CONTENTS P*E&
LIST OF FIGURES ...................................................... 11 LIST OF TABLES ....................................................... iii INTRODUCTION ......................................................... iv 1.0 LIQUID EFFLUENTS 1.1 Liquid Effluent Monitor Setpoints ........................ 1-1 1.1.1 Batch Release Setpoint Determination . .......... 1-2 1.1.2 Continuous Release Setpoint Determination ....... 1-8 1.2 Dose Calculations for Liquid Ef fluents . . . . . . . . . . . . . . . . . . 1-14 1.3 Representative Sampling................................... 1-17 2.0 GASEOUS EFFLUENTS 2.1 Gaseous Ef fluer.t Monitor Setpoints . . . . . . . . . . . . . . . . . . . . . . 2-1 2.1.1 Plant Stack ..................................... 2-1 2.1.2 Condenser Evacuation System ..................... 2-3 2.1.3 Containment Purge ............................... 2-4 2.1.4 Waste Gas Header................................. 2-6 2.2 G a s eous E f flu e nt Dose R ate . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2-11 2.2.1 Noble Gases ..................................... 2-11 2.2.2 Radiciodines and Particulates ................... 2-12 Cl 2.3 Gaseous Effluent Dose calculation ....................... 2-14 2.3.1 Noble Gases ......... 3........................... 2-14 l 2.3.1.1 Histcrical Meteorology ................ 2-14 !
2.3.1.2 Concurrent Meteorology ................. P 15 l i
2.3.2 Radioiodines and Particulates ................... 2-17 '
2.3.2.1 Historical Meteorology ................ 2-17 2.3.2.2 concurrent Meteorology ................ 2-19 i
3.0 PROJECTED DOSES ................................................ 3-1 3.1 Liquid Dose Projection ................................... 3-1 3.2 Gaseous Dose Projection .................................. 3-1 l
l h.3 OPEF. ABILITY OF EQUIPMENT ....................................... 4-1 I
l c. . .n E ga - y ,e - , a e t. . . s s . . n_ pNm
. v a^f.g
- r. s . . _;q.Ie
. ..........n.a p*. ----
.a .......................... ;s .i I
, Rev. 9 l 11-15-82
ODCM .
LIST OF FIGURES Figure Title Page 4-1 SONGS 2&3 Radioactive Liquid Waste Treatment Systems ... 4-2 4-2 SONGS 243 Radioactive Gaseous Waste Treatment Systems .. 4-3 4-3 SONGS 2&3 Solid Waste Handling ......................... 4-4 5-1 Radiological Environmental Sample Locations............. 5-10 11 g a
ODCM LIST OF TABLES Table Title Page 1-1 Liquid Ef fluent Radiation Monitors Calibration Constant.................................... 1-13 1-2 Dose Commitment Factors Ai ............................ 1-16 2-1 Gaseous Effluent Radiation Monitors Calibration Constant.................................... 2-10 2-2 Dose Factors for Noble Gas and Daughters ............... 2-21 2-3 Dose Parameters Pip .................................... 2-22 2-4 Controlling Location Factors ........................... 2-23 2-5 Dose Parameters R f go r W NW S e c t or . . . . . . . . . . . . . . . . . . . . . . 2-24 thru 2-26 2-6 Dose Parameters Ri for !@[ Sectcr ....................... 2-27 thru 2-30 2-7 Dose Parameter R1 for NNW Sector ....................... 2-31 thru 2-34 s 1
2-8 Dose Parameter R i for N Sector ......................... 2-35 [
2-9 Dase Farameter R i for NNE Se: tor ....................... 2-36 i
2-10 Dose Parameter R i for Nj:, Sector ........................ 2-37 l 2-11 Dose rarameter R i for ENE Sector ....................... 2-38 2-12 Dose Parameter Ri for E. Sector ......................... 2-39 ,
I l 2-13 Dose Parameter Ri for ESE Sector ....................... 2 40 thru ,
2-41 i 2-14 Parameters Used to CalcJlate Ri ........................ 2 02 i
- 5-1 Radiological Environnental Monitoring 5-2 thru
( Sample Locations ....................................... 5-7 f
l 5-2 Radiological Environnental Monitoring j Locations .............................................. 5-8 i
- 5-3 Sector ar.d Direction Designation for Radiclogical Environnental
onit or. r g C ample Lc sti;r. " ;- ......................... 5-)
iii p,y, g 11-15-82
INTRODUCTION The OFFSITE DOSE CALCULATION MANUAL (ODCM) is a supporting document of the RADIOLOGICAL EFFLUENT TECHNICAL SPECIFICATIONS (NUREG 0472). The ODCM describes the methodology and parameters to be used in the calculation of offsite doses due to radioactive liquid and gaseous effluents. It also calculates the liquid and gaseous effluent monitoring instrumentation alarm / trip setpoints. The ODCM contains a list of the sample locations for the radiological environmental monitoring program.
The ODCM will be r.aintained at the Station for use as a docu..ent of acceptable methodologies and calculations to be used in implementing the technical specifications. Changes in the calculational methods er parameters will be incorporated into the ODCM in order to assure that the ODCM represents the present methodoloEY.
I"
- Rev. 8 7-1-82
- - - -.-.a - . - . . - -
1.0 LIQUID EFFLUENTS 1.1 Liquid Effluent Monitor Setpoints (3.11.1.1)
Liquid Radwaste Effluent Line Monitors provide alarm and automatic termination of release pricr to exceeding the (
concentration limits specified in '0CFR20, Appendix B. Table II, Column 2 at the release point to the unrestricted area. To meet this specification and for the purpose of implementation of specification 3.11.1.1, the alarm / trip setpoints for liquid effluent monitors and flow measurement devices are set to assure that the following equation is satisfied:
- "3 sC (1-1) where
C= the effluent concentration limit implementing 10CFR20 for the site, in pCi/ml.
c: the setpoint, representative of a radioactivity concentration in pCi/ml , of the radioactivity monitor measuring the radioactivity in the waste effluent line prior to dilution and subsequent release.
I-I Rev. 8 7-1-82
R= the permissible waste effluent flow rate at the radiation monitor location, in volume per unit time in the same units as for F.
F= the dilution water flow in volume per unit time. The available ,
dilution water flow (F) is cot 4stant.
= 207,500 gpm/ pump (x number of cire pumps to be run)
Administrative values are used to reduce each setpoint to account for the potential activity in other releases. These administrative values shall be periodically reviewed based on actual release data (including, for example, any saltwater discharge of the component cooling water heat exchanger) and revised in accordance with the Unit Technical Specifications.
1.1.1 Batch Release Setpoint Determination The waste flow (R) and monitor setpoint (c) are set to meet the condition of equation (1-1) for a given effluent concentration, C. The method by which this is accomp-lished is as follows:
Step 1) The isotopic concentration for each batch tank (or sump) to be released is obtained from the sum of the measured concentrations in the tank (or sump) as determined by analysis.
I-2 Rev. 8 7-1-82
C=ECg g+ C, + C s +Ct+CFe (1-2)
Where: c C = The total concentration
{Cyg=Theconcentrationforeachradionuclide,i,in the gansna spectrum.
C,,
p The Fe-55 concentration as determined in the previous quarterly composite sample.
C = The gross alpha concentration determined in the previous monthly composite sample.
C3= The Sr-89 and Sr-90 concentrations as determined
- in the previous quarterly composite sample.
Ct= The H-3 concentration as determined in the
- previous monthly composite sample.
1-3 g,y, g 7-1-82
Step 2) The adjustment factor, A, for each batch tank (or sump) is determined using:
A= Ig +C s + Cg + C, +C, p (1-3 ) ,
MP( t MPC gi, MPCs, MPCt , = the limiting concentrations of the appropriate HPC p ,, MPC a radionuclide from 10CFR20 Appendix B. Table II, Column 2. For dissolved or entrained noble gases, the concentration shall be limited to 2.0 E-4p Ci/ad. total activity.
Step 3) The radioactivity monitor setpoint may now be specified based on the values of
{Cgg, F. A and R to provide compliance with the limits of 10CFR20, Appendix B Table II, Column
- 2. The monitor setpoint (cpm) is taken from the applicable calibration constants given in Table 1-1 to correspond to the calculated monitor limit C m*
2/3 RT - 7813 0.8 F C,77 m'R A) +R 2 A2 + ... + R A 3
~
Where:
l-N Rev. 8 7-1-82
C,ff = Effective gamma isotopic concentration at the monitor for the tank combination to be released (equal to IC gg for single tank releases).
1 C
R3 ({Cyg), + R2(kgi2*****n(5(in
= (1-5)
R$+R2 + ... + R, (EQgg)3, G Cyg)2 etc. = The total gamma isotopic i i concentration of first tank, second tank, etc.
R j, R2 , etc. = The effluent flow rate from first tank, second tank, etc. Values of R for each tank are as follows:
Radwaste primary tanks R = 140 gpm/ pump (x no. of pumps to be run)
Radwaste secondary tanks R = 140 gpm/ pump (x no. of pumps to be run)
- Primary plant makeup tanks R = 160 gpm/ pump (x no. of pumps to be run)
Condensate monitor tanks R = 100 gpm/ pump (x no. of pumps a to be run) 1-5 Rev. 8 7-1-82
l A j , A 2, etc. = Value of A from equation (1-3) for first tank, second tank, etc.
The 0.8 is an administrative value used to ,
account for the potential activity for ott.er releases. This assures that the total concentra-tion from all release points to the plant discharge will not result in a release of concen-trations exceeding the limits of 10CFR20, Appendix B. Table II, Column 2 from the site.
NOTE: If Cmj(C,ff then no release is possible. To increase C m, increase dilution flow F (by running more circulating water pumps in the applicable discharge structure), and/or decrease the effluent flow rates R g , R p ,
etc. (by throttling the combined flow as measured on 2/3 FI-7643), and recalculate C,using the new F. R and equation (1-4).
l-0 Rev. 8 7-1-82
If there is no release associated with this monitor, the monitor setpoint should be established as close to background as practical to prevent ,
spurious alarms and yet assure an alarm should an inadvertant release occur.
2RT - 7817, 3RT - 7817 9
(0.5) (0.1)F{Cgg C <
-6)
Where:
IC gt, A = The values of {C g and A (as defined in Steps 1) and 2) above) for the neutralization sump. R = 400 gpm/ pump (x number of sump pumps to be run).
The 0.1 is an administrative value used to account for the potential activity from other releases. This assures that the total concentration from all release points to the plant discharge will not result in a release of concentrations exceeding the limits of 10CFR20, Appendix B. Table II, Column 2 from the site.
0.5 is an administrative value used to account for 9
simultaneous releases from both SONGS 2 and SONGS 3.
1-7 g,y, 9 11-15-82
NOTE: If C, < { Cyg then no release is possible. To increase C,, increase dilution flow F (by running more circulating water pumps), and/or .
decrease the effluent flow rate R (by throttling the flow as measured on 2FI 3772 and 3FI 3772), and recalculate i C, using the new F, R and equation (1-6).
If there is no release associated with this monitor, the monitor setpoint should be established an close to background as practical to prevent spurious alarms and yet assure an alarm should an inadvertant release occur.
1.1.2 Continuous Release Setpoint Determination l
l Step 1) The isotopic concentration for the continuous releases are obtained for each release stream (steam generator blowdown or turbine building sump) from the sum of the respective measured concentrations as determined by analysis:
C = { Cyg + C, + Ct+C 3 +C Fe (I-I}
l-0 Rev. 9 11-15-82
where:
Cgg = the total gamma activity ( p Ci/ce) associated with each radionuclide, i, in the weekly composite analysis for the release stream. <
C, = The total measured gross alpha concentration (pCi/cc) determined from the previous monthly composite analysis for the release stream.
Cp,= The total Fe-55 concentration as determined in the previous quarterly composite sample for the release stream.
Ct= the total measured H-3 concentration (pci/ce) i determined from the previous monthly composite analysis for the release stream.
C3= the total measured concentration (pCi/cc) of Sr-89 and Sr-90 as determined from the previous l quarterly composite analysis for the release 1
l I
stream.
l l
1 l
1-9 Rev. 8 7-1-82 1
. ~. _
l Step 2) The adjustment factor, B, for each release stream (steam generator blowdown or turbine l building sump) is determined using:
P B= IC gg + C, + C C, + C, p (1-8 )
t MPC MPC, MPC MPC, MPC t Fe Step 3) The setpoint for each continuous release radioactivity monitor may now be specified based on the respective values of {C g. F. B and R to provide compliance with the limits of 10CFR50, Appendix B. Table II, Column 2. The monitor setpoint (cpm) is taken from the applicable calibration constants given in Table 1-1 to correspond to the calculated monitor limit, C m-2RT - 7817, 3RT - 7817 9
C, _1 (0.5) (0.1)F{Cgi (j_9)
RB Where:
ICygB = values of IC yg and B (as defined in i i Steps 1 and 2 above) for the steam generator blowdown. ,
1-10 p,y, 9 11-15-82
J. ~s R = 400 gpm where R is the effluent flow rate at the radiation monitor as defined in Step 2. '
The 0.1 is an administrative value to account for the pctential activity in other release pathways. This assures that the total concentration from all release points to the plant discharge will not result in a release of concentrations exceeding the limits of 10CFR20, Appendix B, Table II, Column 2 from the site.
0.5 is an administrative value used to account for i
simultaneous releases from both SONGS 2 and SONGS 3 NOTE: C, < { C 1 then no release is possible. To increase C m , increase the dilution flow F (by running more circulating water pumps), and/or decrease the effluent flow rate R (by throctling the flow as measured on 2FI-3772),
and recalculate Cm using the new values of F R-and equation (1-9).
2RT - 7821, 3RT - 7821 9
C < (0.5) (0.1)F{C(1 ~
RB l~ll Rev. 9 11-15-82 I
-~ - --
Where:
ICyg, B = values ot~ ICgg and B (as defined in i i ateps 1) and 2) above) for the turbine ,
building sump a
l R = 50 spm/ pump (x no. sump pumps to be run)
The 0.1 is an administrative value to account for the potential activity in other release pathways. This assures that the total concentration from all release points to the plant discharge will not result in a release of concentrations exceeding the limits of 10CFR20, Appendix B, Table II, Column 2 from the site.
0.5 is an administrative value used to account for simultaneous releases from both SONGS 2 and SONGS 3.
NOTE: If C, < {Cgg then no release is possible. To increase Cm , increase the dilution flow F (by running more circulating water pumps) and recalculate Cm using the new value of F and equation (1-10).
1-12 Rev. 8 7-1-82
Table 1-1 Liquid Effluent Radiation Monitor Calibration Constants M
Monitor Co-60' Be-133' Cs-137' n
2/3RT-7813 2.08 E-9 3.14 E-9 4.59 E-9 ,
2RT-7817 2.11 E-9 3.20 E-9 4.71 E-9 2RT-7821 2.08 E-9 3.17 E-9 4.61 E-9 3RT-7817 2.24 E-9 2.99 E-9 4.63 E-9 '
3RT-7821 2.15 E-9 3.30 E-9 4.72 E-9
'uCi/cc/ cpm 1-13 g,y, 9 11-15-82
1.2 Dose Calculation for Liquid Effluents (3.11.1.2)
The dose comunitment to an individual from radioactive materials in liquid effluents released to unrestricted areas are calculated for c the purpose of implementing Specification 3.11.1.2 using the following expression.
D, = { [{ { (At yCyy Fy )] (1-9) where:
A gT = the site related adult ingestion dose committment factor to the total body or an organ, t, for each identified principal gama and beta emitter, i, from Table 1-2 in mrem /hr per p Ci/ml.
C gy = the average concentration of radionuclide, i,
, in the undiluted liquid effluent during time period.
At y in yCi/ml.
t D = the dose commitment to the total body or an organ, t, from the liquid effluents for the time period, At y, in mrem.
l l-l" l Rev. 8 7-1-82 i
l
.n-F3 = the near field average dilution factor for Cgy during the time period, at y. This factor is the ratio of the maximum undiluted liquid waste flow during time period, At y, to the average flow from the site discharge structure to unrestricted receiving waters or
, maximum liquid radioactive waste flow discharge structure exit flow at y = the length of the I th time period over which Ciy and F1 are averaged for all liquid releases, in hours.
l 1-15 Rev. 8 7-1-82
TAKE 1-2 DOE CONTDeff FACIDRS. A gT (mravhr per pCi/ml)
Radio- Total GI-Nuclid Bofy Bone Liver 'lhyroid Kidney Img LLI H- 3 2.80 E1 2.80 E-1 2.80 E-1 2.80 E-1 2.80 E-1 2.80 E-1 P - 32 6.46 E+5 1.67 E+7 1.04 L6 1.88 E46 Cr - 51 5.60 3.30 1.20 7.40 1.40 E+3
- - 54 1.35 D3 7.08 E+3 2.11 E+3 2.17 E4 Fe - 55 8.24 E+3 5.12 EA 3.53 EA 1.77 E4 2.03 E 4 Fe - 59 7.27 E4 8.07 E A 1.90 E+5 5.30 E4 6.23 L 5 Co - 58 1.35 E+3 6.04 D2 1.22 E4 Co - 60 3.83 E+3 1.74 E+3 3.26 E4 2n - 65 2.32 E+5 1.61 E+5 5.13 E+5 3.43 E+5 3.23 b 5 Rb - 86 3.02 E+2 6.48 E+2 1.28 E42 Sr - 89 1.43 E+2 4.99 b3 8.00 E+2 Sr - 90 3.01 EA 1.23 L5 3.55 D3 Y - 91 2.38 8.90 E+1 4.90 E 4 Zr - 95 3.47 1.60 E+1 5.12 8.03 1.62 E4 -
Zr - 77 8.14 E-2 8.80 E-1 1.80 E+1 2.70 E-1 5.51 E4 Nb - 95 1.34 L2 4.48 L2 2.49 L2 2.46 E42 1.51 D6 6 - 99 2.44 E+1 1.28 D2 2.90 E+2 2.77 D2 lb - 103 4.61 D1 1.07 E42 4.08 E42 1.25 E+4 lb - 106 2.01 E+2 1.59 E+3 3.C7 E+3 1.03 b 5 .
Ag - 110m 8.61 L2 1.57 E+3 1.45 E+3 2.85 E+3 5.91 E+5 Sb - 124 1.10 E+2 2.7/ D2 5.23 6.70 E-1 , 7.85 E+3 Sb - 125 4.42 E+1 2.20 L2 2.37 2.00 E-1 2.30. L 4 1.94 E+3 Te - 125to 2.91 51 2.17 E+2 7.87 E+1 6.54 E+1 8.84 E+2 8.68 E+2 Te - 127m 6.69 D1 5.49 E42 1.95 L2 1.40 E42 2.23 E+3 1.84 D3 Te - 129m 1.48 E+2 9.33 D 2 3.48 D2 3.20 E+2 3.89 E+3 4.67 b 3 Te - 131m 5.72 D1 1.40 L2 6.88 E+1 1.09 E42 6.95 E+2 6.81 E+3 Te - 132 1.24 E+2 2.40 E+2 1.32 E+2 1.46 D 2 1.27 E+3 6.25 E+3 I - 131 1.79 E42 2.18 E+2 3.12 E+2 1.02 DS 5.36 L 2 8.24 E+1 I - 133 3.95 E+1 7.46 E+1 1.30 E+2 1.91 E4 2.26 D 2 1.17 E+2 Cs - 134 1.33 E4 6.84 E+3 1.63 E4 5.27 E+3 1.75 5 3 2.85 L2 Cs - 136 2.04 E+3 7.16 E+2 2.83 D3 1.57 E+3 2.16 D 2 3.21 E+2 Cs - 1J7 7.85 E+3 8.77 E+3 1.20 E+4 4.07 E+3 1.35 E+3 2.32 D2 Ba - 140 1.08 E+2 1.65 E+3 2.07 7.00 E-1 1.18 3.39 E+3 La - 140 2.10 E-1 1.58 8.00 E-1 5.84 E4 Ce - 141 2.60 E-1 3.43 2.32 1.08 8.86 E+3 Ce - 143 4.94 L2 6.00 E-1 4.tr7 E-2 2.00 E-1 1.67 Ed Ce - 144 9.59 1.99 E+2 7.47 b1 4.43 E+1 6.04 E+4 Np - 239 1.E E-3 3.53 E-2 3.tr7 E-3 1.08 E-2 7.13 L2 1-16 Rev. 8 7-1-82
1.3 Representative Sampling Prior to sampling of a batch release, each batch shall be thoroughly mixed to assure representative sampling. The methodology for mixing and sampling is described in SO23 III - 5.4.23 Liquid Radwaste Sampling.
i l
l t
1-17 Rev. 8 7-1-82
2.0 GASEOUS EFFLUENTS 2.1 G3 f eous Effluent Monitor Setpoints (3.11.2.1)
Administrative values are used to reduce each setpoint to account for the potential activity in other releases. These administrative values shall be periodically reviewed based on actual release data and revised in accordance with the Unit Technical Specifications.
2.1.1 Plant Stack - 2/3RT - 7808, 2RT-7865-1. 3RT-7865-1 For the purpose of implementation of Specification 3.11.2.1, the alarm setpoint level for noble gas monitors is based on the gaseous effluent flew rate and
.etecrological dispersien factor.
The concentration at the detector is determined by using:
(MPC) (2-1)
C < (0.45) (2120) (X/Q) (flow rate) l l
l where:
C = the instantaneous concentration at the detector in pCi/cc
~
Rev. 8 7-1-82
MPC = the 10CFR Part 20 concentration for the limiting c
radionuclide present in sample analysis in uCi/cc (i.e., smallest MPC) flow rate = the plant vent flow rate in efm
= 83,000 cfm/ fan (x no. of fans to be run)
(X/Q) = 2.4 E-5 sec/m 3 the annual average atmosphere dispersion 2120 = conversion of cfm to m3f3,e 0.45 is an administrative value used to account for potential activity from other gaseous release pathways The alarm setting is deterr ined by using the calibration constant for the applicable Plant Stack Airborne Monitor given in Table 2-1. The alarm setpoint is the epm value corresponding to the concentration, C, which is conservatively assumed to be the isetepe cf greatest sensitivity for the nenitor.
If there is no release associated with this monitor, the monitor setpoint should be established as close as practical to 9 background to prevent spurious alarms and yet assure an alarm should inadvertant release occur.
E~I Rev. 9 11-15-82
2.1.2 Condenser Evacuation System - 2RT - 7818, 2RT - 7870-1 ((
3RT - 7818 or 3RT - 7870-1 For the purpose of implementation of Specification 3.11.2.1, the alarm setpoint level for noble gas monitors is based on the gaseous effluent flow rate and meteorological dispersion factor.
The concentration at the detector is determined by using:
(2-2)
C < (0.1) (0.5) (2120) (x/Q) fffowrate) where:
C = the instantaneous concentration at the detector in pCi/cc MPC = the 10CFR Part 20 concentration for the limiting r.!idionuclide present in sample analysis in pCi/cc (i.e., smallest MPC) flow rate = the condenser evacuation system flow rate in efm
= 1,000 cfr.
(X/Q) = 2.4 E-5 sec/m 3 the annual average atmosphere dispersion l
2120 = conversion of cfm to n 3/sec l
2-3 gey, 9 11-15-82 l
0.1 is an administrative value used to account for potential activity from other gaseous release pathways.
0.5 is an administrative value used to account for releases from 'l both SONGS 2 and SONGS 3 simultaneous.
The alarm setting is determined by using the calibration constant for the corresponding Condenser Evacuatien System Monitor given in Table 2-1. The alarm setpoint is the epm value corresponding to the concentration, C, which is conservatively assumed to be the isotope of greatest sensitivity for the monitor.
If there is no release associated with this monitor, the monitor setpoint should be established as close as practical to i background to prevent spurious alarms yet assure an alarm should I
an inadvertent release occur.
e1 2.1.3 Containment Purge - 2RT - 7804-1, 3RT - 7804-1 l
For the purpose of implementation of Specification l
3.11.2.1, the alarm setpoint level for noble gas monitors i
! is based on the gar *'.: effluent f':w rate ar.d l meteorological dispersion factor, i
The concentration at the detector is determined by using:
l fup*
~ ' ' '
C < '
' '. . L 5 ) (0.5) (2127> (2-? 9 (X/.. (fice rate) 2-4 Rev. 9 11-15-82
where:
C = the instantaneous concentration at the detector in pCi/cc MPC = the 10CFR Part 20 concentration for the limiting radionuclide present in sample analysis in pCi/cc.
(i .e. , smallest MPC) flow rate = the containment purge flow rate in efm
= 40,000 cfm full purge
= 2,000 cfh mini purge (X/Q) = 2.4 E-5 sec/m3 the annual average atmosphere dispersion 3
2120 = conversion of efb to m f3,c 0.45 is an administrative value used to account for potential activity from other gasecus release pathways.
0.5 is an administrative value used to account for simultaneous q releases from both SONGS 2 and SONGS 3 The alarm setting is determined by using the calibration constant for t".e Containment Airborne Mcniter giver, in Table 2 1 The alarm setpoint is the epm value corresponding to the concentration, C, which is conservatively assumed to be the isotope of greatest sensitivity for the monitor.
2-5 g,y, 9 11-15-82
If there is r.o release associated with this monitor, the monitor setpoint should be established as close as practical to T background to prevent spurious alarms yet assure an alarm should an inadvertent release occur.
2.1.4 Waste Gas Header - 2/3 RT-7814, 2/3 RT-7808 For the purpose of Specification 3.11.2.1, the alarm setpoint level for noble gas monitors is based on the gaseous effluent flow rate and meteorological dispersion factor. Since the waste gas header discharges to the plant vent stack, either 2/3 RT-7814 or 2/3 RT-7808 may be used to monitor waste gas header releases.
2/3 RT-7808 When plant vent stack monitor 2/3 RT-7808 is being used to F.onitor waste gas header releases, the setroint determined by equation (2-1) will provide automatic te'rminatien of release frcm the waste gas header.
s Determine the maximum permissible waste gas header effluent flow rate corresponding to the vent stack nonitor setpoint in accordance with the fellcwing:
fg (0.9) C F (2 4) j C 21 8
2-6 Rev. 9 11-15-82
Where:
f = waste gas header effluent flow rate F = plant vent stack flow rate used in equation (2-1)
{Cfg = total gamma activity ( uCi/cc) of the waste gas holdup tank to be released, as determined from the pre-release sample analysis.
The 0.9 is an administrative value to account for the potential activity from other releases in the sane release pathway.
2/3 RT-7814 C < (0.9) (0.45) (2120) (= /0) ( [owrate) (2-5)
, iTnere :
C = the instantaneous concentration at the detector in pC1/cc M PC = the 10CFR20 concentration for the limiting radionuclide present in the sample analysis in p C1/cc (i.e., smallest MPC) flow rate = the waste gas header flow rate in eft
= 50 cfm (X/0) 2.4 E-5 sec/m 3 . the a.r.ual average atmosphere disperrion 2-7 h13*8b
2120 = conversion of cfm to m 3 /sec
-The 0.45 is an administrative value to account for potential activity from other release pathways.
The 0.9 is an administrative value to account for potential activity from other gaseous releases in the same release pathway.
The alarm setting is determined by using the calibration constant for the Waste Gas Header Monitor given in Table 2-1. The alarm setpoint is the epm value corresponding to the concentration, C, which is conservatively assumed to be the isotope of greatest sensitivity for the monitor.
NOTE: If C < jC g for the waste gas decay tank, then no release is
, possible. To increase C, decrease the waste gas effuent flew rate in accordance with:
( f1 rate) <
(0.9) (0.45) (2120) MPC ,2-6)
{C g (X/Q)
Where:
flow rate = tne maximum per.missible waste gas effluer.t flow rate in efi.
0.9, 0.45, 2120, MPC. X/Q are defined in equation (2-5)
E~0 Rev. 8 7-1-82
{Cgg= total gamna activity (uCi/ce) of the waste gas holdup tank to be released, as determined from the pre-released sample analysis.
Recalculate the monitor setpoint using the new flow rate and equation (2-5).
If there is no release associated with this monitor, the monitor setpoint should be established as close as prcetical to background to prevent spurious alarms and yet assure an alarm should an inadvertant release occur.
i f
2-9 Rev. 8 7-1-82
e o ,
Table 2-1 Gaseous Effluent Padiation Monitor Calibration Constants Monitor Kr-85' Xe-133' 2RT-7804-1C 2.78 E-8 3.90 E-8 3RT-7804-1C 2.05 E-8 1.67 E-8 9 2/3RT-7808C 2.76 E-8 3.72 E-8 2/3RT-7814A 3.21 E-8 4.49 E-8 2/3RT-7814B 4.24 E-5 3.61 E-5 2RT-7818A 3.06 E-8 5.30 E-8 2RT-7818B 5.85 E-5 3. 77 E-5 3RT-7818A 3.14 E-8 4.56 E-8 3RT-7818B 3.00 E-5 2.83 E-5 2RT-7865-1 (low) 1.41 E-8 3.02 E-8 2RT-7865-1 (mid) 5.33 E-5 2RT-7865-1 (high) 6.81 E-2 3RT-7865-1 (low) 1.41 E-8 3.02 E-8 3RT-7855-1 (mid) 8.02 E-5 3RT-7865-1 (high) 2.39 E-2 2ET-75 :-1 ,2 ws ".,1 E-5 3.02 E-5 2RT-7870-1 (mic) 1.07 E-4 2RT-7570-1 (hign) 2.67 E-2 3RT-7870-1 (low) 1.41 E-8 3.02 E-8 T 3RT-7870-1 (mid) 1.05 E-4 3RT-7870-1 (high) 2.17 E-2
'uCi/cc/ cpm 2-10 3,y, 9 11-15-82
2.2 Gaseous Effluents Dose Rate (3 11.2.1)
The methodology used for the purpose of implementation of Specification 3 11.2.1 for the dose rate above background to an individual in an unrestricted area is calculated by using the following expressions:
2.2.1 For noble gases:
I DTB
- k i *#0) i (2-7}
D 3 ={[ (Lg + 1.1M )g (x /Q) Q g3 (2-8) where:
Ei = the total body dose factor dae to gamma emissions for each identified noole gas radionuclide, in 1
mrem /yr per p Ci/m- from Table 2-2 Li = skin dose factor due to the beta emissions for each identified noble gas radionuclide in mrem /yr per uCi/m 3 from Table 2-2.
2-Il Rev. 8 7-1-82
M i = the air dose factor due to gamma emissions for each identified noble gas radionuclide, in mrad /yr per 3
pC1/m from Table 2-2.
(Unit conversion constant of 1.1 mrem / mrad converts air dose to skin dose.)
Di = the release rate of eadionuclide, i, in gaseous effluents in pCi/sec (X/Q) = 2.4 E-5 sec/m3 . The highest calculated annual average relative concentration for any area at or beyond the unrestricted area boundary DB = total body dose rate in unrestricted areas due to radioactive materials released in gaseous effluents, in mrem /yr 1
0 3
= skin dose rate i. unrestricted areas due to radioactive mate-ials release: in Saseous effluents, in mrem /yr 2.2.2 For all radioiodines, radioactive caterials in particulate form, and radionuclides other than noble gases with half lives greater than eight days:
I Do= I[IP 1p p73D 1 (2-9) i k 2-12 Rev. 8 7-1-82
where:
Do = organ dose rate in unrestricted areas due to radioactive materials released in gaseous effluents, in mrem /yr Di = the release rate of radionuclide, i, in gaseous effluents in pCi/sec Pik = the dose parameter for radionuclide, i, for pathway, k, from Table 2-3 for the inhalation pathway in mrem /yr per pCi/m3 . The dose factors are based on the critical individual organ and the child age group.
5k= the highest calculated annual aver age dispersion parameter for est. atir.g the dese t: an individual at or beyond the enrestricted a es tc;ndary for 4
pathway at, k.
= 2 3 E-5 sec/m3 for the inhalation pathway.
4 The location is the unrestricted area in the NNW sector.
= 1.5 E-7 m-2 for the food and groar.d plane pathways.
The location is the unrestricted area in the ESE sector.
2-13 p,y, g 7-1-82
2.3 Gaseous Effluent Dose Calculation 2.3.1 Dose from koble Gases in Gaseous Effluent (3.11.2.2)
The air dose in unrestricted areas due to noble gases released in gaseous effluents is calculated using the i
following exprer.-ions:
2 3.1.1 For historical methodology:
-8 (2-10)
Dy = 3.17 x 10 M 3 ((x/0) 0 )
-8 D
3= 3.17 x 10 IN ((x/0) C) (2-11) i where:
- = :ne t;tal projecte: Es- .s ai- de:e fr:r Y
gaseous effluents, in :-ad O. = the total projected beta air dose from gaseous ef fluer.ts, ir. - ad 2-Rev. 8 7-1-82
M = t' ' air dose fcctor due to st=ma er.is-sions for each identified noble gas radionuclide, i, in mrad /yr pe.-
uCi/m3 in Table 2-2 Ng = the air dose due to beta emis-ssions for each identified noble radionuclide, i, in mrad /yr per pCi/m3 from Table 2-2 (X/Q) = 2.4 E-5 sec/m3 . The highest calculated annual average relative concentration for any area at or beyond the unre-stricted area boundary.
0; = the a rant of .otle gas radio.uclide,
- 2. released in Easeous effluents in uC1.
2.3.1.2 For meteorology concurrent with release:
D g = 1.14x10 IM3(I (4t) (X/Q))g Dg ) ') (2 *2)
. J D SS
= 1.14 x10 ' I Ni (I (atJ (X/0) >- Q i .i) , (2 1L i )
2-10 Fev. E 7-1-82
where:
D g = the total gamma air dose from gaseous effluents in sector 0, in mrad DSB = the total beta air dose from gaseous effluents sector 8, in mrad M g= the air dose factor due to gamma emis-sions for each identified noble gas radionuclide, i, in mrad /yr per uCi/m3 from Table 2-2 N g= the air dose factor due to beta emissions for each identified noble gas radionuclide, i, in mead /yr per a Ci /m fren Table 2-2 th at = the length of the j time period over which (X/Q) andb are averaged je ij for gaseous releases in hours (x/Q))g = the atmospheric dispersior. factor for time period Atj at exclusion boundary location in sector 6 i
determined by concurrent meteorology, in sec/n3 2-16 g,y, g 7-1-82
- the average release rate of Q)g radionuclide, i, in gaseous effluents during time period, at), in pCi/sec 2.3 2 Dose from Radioiodines. Radioactive Material in Particulate Form, and Radionuclides other than Noble Gases in Gaseous Effluents. (3.11.2.3)
The dose to an individual from radioiodines, radioactive materials in particulate form and all radionuclides other than noble gases with half lives greater than eight days in gaseous effluents released to unrestricted areas is calculated using the following expressions:
2.3.2.1 For historical neteorology:
D o = 3.17x10-0 { [(I Rikwx} 0 13 (2-14) where:
D3 = the total projected dose from gaseous efflaents to an individual, in mren 2-17 hi"8h
Qi = the amount of radiciodines, radioactive materials in particulate form and radionuclides other than noble gases with half lives greater than eight days, i, released in gaseous effluents in pCi
{R ik Wk = the sum of all pathways k for radionuclide, i, of the R g, W product in mrem /yr per pCi/sec. The gRik"k value for each radionuc'.ide, i, is given in Table 2-4 The given is the maximum {Rikwk f r all locations and is based on the most restrictive age groups.
R ik = the dose factor for each identified radionuclide, i, for pathway k (for the irhalatier. pathway in mrem /yr per p Ci/m3 and for the food and ground plane pathways in m - crem/yr per pCi/sec) at the controlling location. The Rik's for each controlling location for each age group are given in Tables 2-5 thru 2-13 Wk = the annual average dispersion parameter fer estimating the dose to an individual at the controlling location for pathway k.
2-18 h'l *-8h
O
= (X/Q) for the inhalation pathway in sec/m 3, The TX/Q) for each controlling location are given in Tables 2-5 thru 2-13
= (D/Q) for the food and gr:arnd plane pathways in m-2 The (D/Q) for each controlling location are given in Tables 2-5 thru 2-13 2 3 2.2 For meteorology concurrent with releases.
D o = 1.14x10-" { [ gat)([ Rike " M } bij) (2-15) where:
D3 = the total annual dose fron i;aseous effluents te an individual in sector 5 in trem.
th period over which at) = the length of the j W and Q1 ) are averaged for gaseous jks releases in hours Dg ) = the average release rate of radionuclide, i, in gaseous effluents during time period at) in aci/sec f
2-19 Rev. 8 7-1-82
Rik6 = the dose factor for each identified radionuclide i, for pathway k for sector 0 (for the inhalation pathway in mrem /yr per yCi/m3 and for the food and ground plane pathways in m 2mrem /yr per pCi/sec) at the controlling location.
A listing of Rik for the controlling locations in each landward sector for each group is given in Tables 2-5 thru 2-13 The Ois determined by the con-current meteorology.
W jke = the dispersion parameters for the time at) period for each pathway k for calculating the dose to an individual at the controlling location. in sector 9 using concorrer.t r.etecr:'.:;ical conditions.
= (X /Q) for the inhalation pathway in sec/m3
= (D/0) for the food ara secur.: plar.e pathways in m-2 2-20 hi'8h
TAB 2 2-2 DWE FACERS F3 NORI MSE:5 A'O DWGHIUtS Total Body Dose 3dn Eose Gama Air Dose Beta Air Dose Radio - Factor Kg Factor Li Factor Mi Factor Ng nuclide (wevyr per pCiM) (revyr per pCiM) (rad /yr per pCi/m3) (rad /yr per pCiM)
Kr- 83m 7.56 E-28 1.93 E+1 2.88E+2 Kn- 85m 1.17 E+3 1.46 E+3 1.23 E+3 1.97 E+3 Kr- 85 1.61 E+1 1.34 E+3 1.72 E+1 1.95 E+3 Kr- 87 5.92 E+3 9.73 E+3 6.17 E+3 1.03 E+4 Kr- 88 1.47 E4 2.37 E+3 1.52 E+4 2.93 E+3 Kr- 89 1.66 E4 R01 E4 1.73 E+4 1.06 E 4 Kr- 90 1.% E+4 7.29 E+3 1.63 E4 7.83 E+3 Xe- 131m 9.15 E+1 4.76 E+2 1,56 E+2 1.11 E+3 Xe- 133n 2.51 E4 9.c4 E+2 3.27 E+2 1. 4 E+3 Xe ~33 2.~e E+2 3.06 E+2 3.53 E+2 1.3 E+3 Xe- 135n 3 12 E+3 7.11 E4 3 36 E+3 7.39 E+2 Xe- 135 1.81 E+3 1.86 E+3 1.92 E+3 2.46 E+3 Xe- 117 1.42 E+3 1.22 E+4 1.51 E+3 1.27 E+4 Xe- 138 8.83 E+3 4.13 E+3 9.21 E+3 4.75 E+3 Ar- 41 8.84 E+3 2.69 E+3 9.30 E+3 3.28 E+3 i
0 7.56 x 194 = 7.56 E-2 2-21 p,y, 3 7-1-82
TARI 21 DOE PARAPET 3t Pg OiILD NE CROUP Inhalaticri Pathay Inhalation Patha y Radienuclide (urun/yr per pCiM) Radiruelide (nrem/yr per pCiM)
H-3 1.1 E+3 Tc - 101 5.8 E+2 C - 14 3.6 E 4 Ru - 103 6.6 E+5 Na - 24 1.6 E4 Ru -- 105 1.0 E+5 P - 32 2.6 E+6 Ru. 106 1.4 E+7 Cr - 54 1.7 E4 Ag - 110M 5.5 E+6 h - 54 1.6 E+6 Te - 125H 4.8 E+5
- - 56 1.2 E+5 Te - 127M 1.5 E+6 Fe - 55 1.1 E+5 Te - 127 5.6 E4 Fe - 59 1.7 E+6 Te - 129M 1.8 E46 Co - 58 1.1 E+6 Te - 129 2.5 E+4 Co - 60 7.1 E+1 Te - 131M 3.1 E+5 Ni - 63 8.2 E+5 Te - 131 2.1 E+3 Ni - 65 8.4 Ed Te - 132 3.8 E+5 Cb - 64 3.7 E+4 I - 130 1.8 E+6 Zn - 65 1.0 E+6 I - 31 1.6 E+7 Zn - 69 1.0 E+4 I - 132 1.9 E+5 Br - 83 4.7 E+2 I - 1J3 3.8 E+6 Br - SL 5.5 E+2 I - 134 5.1 E4 Br - S5 2.5 E+1 I - 135 7.9 E4 Eb - 86 2.0 E+5 Cs - 134 1.0 E+6 Rb - 88 5.6 E42 Cs - 136 1.7 E 5 Rb - 89 3.5 E.2 Cs - 137 9.1 E+5 Sr - 89 2.2 E+6 Cs - 138 8.4 E+2 Sr - 90 1.0 E+8 Ba - 139 5.8 E+4 Sr - 91 1.7 E+5 Ba - 140 1.7 E+6 Sr - T 2.4 E+5 Ba - 141 2.9 E+3 Y - 90 2.7 E+5 Ba - 142 1.6 E+3 Y - 91M 2.8 E+3 La - 140 2.3 E+5 Y - 91 2.6 E46 La - 142 7.6 E+4 Y -9 2.4 E5 Ce - 141 5.u E.5 Y - 93 3.9 E+5 Ce - 143 1.3 E+5 Zr - 95 2.2 E46 Ce - 144 1.2 E+7 Zr - 97 3.5 E+5 Pr - 143 4.3 E+5 Nb - 95 6.1 E+5 Pr - 144 1.6 E+3 Mo - 99 1.4 E+5 Nd - 147 3.3 E+5 Tc - 99M 4.8 E+3 W -1Er7 9.1 E4 Np - 239 6.4 E4 2-22 Rev. 8 7-1-82
TABII 2 4 QJPml0LLDC IDCATION FA~IDRS Rik N Radionuclide r yr per pCi/sec H-3 1.5 E-3 CN 51 1.5 E-1 h 54 2.0 E+1 Fe- 59 1.1 E+1 Co-58 8.9 Co- 60 2.2 E4 Zn- 65 31 E+1
&- 89 31 E4 Sn- 90 1.3 E+4 Ir- 95 1.3 E+1 St>-124 3.2 E+1 I -131 5.8 E4 I -133 5.6 E+1 Cs-134 2.9 E4 Cs-136 3.7 Cs-137 3.0 E-2 i
Ba-luo 31 Ce-141 5.1 1.hidentified 1.2 E4 1
l Footnote: These values to te used in rmm1 calculations a-e the raxi.u. ;g F ^9 Kg for all locations based on the most, restrictive age gm.p.
2-23 Rev. 8 7-1-82
1 Page 1 of 3 TABLI 2-5 Ibse Pa riete- R i for g Sec'.or Path ey Ss) Onoth Beam Dista1ce 0.48 miles X4 1.1E-5 D/0 2.5 E4 Infant 0111d Teen Adult iadionuclide Inhalatim Food & Gmad Inhalatim Food & Grotid Inhalation Food & Grotid Inhalaticri Food & Gmrid
'Pathay HPathay Pathay Pathay Pathuey Pathay Pathay Pat % y H -
3 1.5 E42 0 2.6 E4 0 2.4 E4 0 2.9 E4 0 P - 32 4.6 E+5 0 5.9 E+5 0 4.3 E+5 0 30 E+5 0 Cr - 51 8.2 E+1 1.1 E+6 2.5 E+2 1.1 E+6 6.8 E+2 1.1 E+6 7.6 E42 1.1 E+6 H2 - 54 5.8 E+3 3 2 E+8 9.8 E+3 3.2 E+8 1.5 E4 3.2 E+8 1.8 E 4 3.2 E+8 F2 - 59 5.4 E+3 6.2 E+7 7.6 E+3 6.2 E+7 4.1 E4 6.2 E+7 4.3 E44 6.2 E+7 Co - 58 2.5 E+3 8.7 E+7 7.8 E+3 8.7 E+7 2.2 E4 8.7 E+7 2.4 E4 8.7 E+7 Co - 60 7.3 E+3 4.9 E+9 2.2 E4 4.9 E+9 5.9 E4 4.9 E+9 6.5 E4 4.9 E+9 Zn - 65 1.4 E+4 1.7 E+8 2.6 E 4 1.7 E+8 3.1 E4 1.7 E+8 2.4 E+4 1.7 E+8 Rb - 86 4.3 E4 2.1 E+6 4.5 E4 2.1 E+6 4.3 E+4 2.1 E+6 3.1 E4 2.1 E+6
&- 89 9.1 E4 4.9 E+3 1.4 E+5 4.9 E+3 9.9 E44 4.9 E+3 6.9 E 4 4.9 E+3 Sr - 90 9.3 E+6 0 2.3 E+7 0 2.5 E+7 0 2.3 E+7 0 Y - 91 1.6 E 4 2.3 E+5 4.2 E4 2.5 E+5 9.3 E 4 2.5 E+5 8.8 E 4 2.5 E+5 Zr - 95 5.0 E+3 5.7 E+7 1.4 E4 5.7 E+7 3.4 E+4 5.7 E+7 3.4 E4 5.7 E+7 Nb - 95 2.9 E+3 31 E+7 8.4 E+3 3.1 E+7 2.2 E+4 3.1 E+7 L4 E+4 3.1 E+7 Ru - 103 3.7 E+3 2.5 E+7 1.0 E4 2.5 E+7 2.5 E4 2.5 E+7 2.5 E44 2.5 E+7 Ru - 106 3.7 E 4 4.7 E+7 9.8 E4 9.7 E+7 2.2 E+5 9.7 E+7 2.1 E45 9.7 E+7 Ag - lim 7.5 E+3 7.9 E+B 2.3 E4 7.9 E+8 6.2 E4 7.9 E 3 6.9 E4 7.9 E+8 cd - 11 3 1.6 E4 0 4.2 E4 0 9.3 E+4 c 8.0 E 4 0 Sn - 123 6.7 E+4 0 1.1 E+5 0 7.6 E+4 0 7.2 E+4 0 Sn - 126 2.7 E+5 6.~ E4 9.3 E+5 6.^ E9 4.n E+5 '^E9
. 2.9 I 4 f.3 E4 3d - 124 1.3 E+4 1.- E4 3.7 E-4 1.4 E4 9.1 E- ".4 E-: 9.3 E4 *4 E4 2 - 125 3.4 E+3 5.3 E+E 4.2 E+3 5.3 E-6 2.3 E+4 5.3 E-8 2.3 E4 5.3 E4 Te - 127M 8.6 E+3 2.1 E+4 1.5 E4 2.1 E4 1.5 E4 2.1 E- 1.0 E4 2.1 E+4 T2 - 1291 7.3 E+3 4.5 E+6 1.1 E4 4.5 E+6 1.2 E4 4.5 E4 8.3 E+3 4.5 E+6 Cs - 134 1.6 E+5 1.6 E+4 2.3 E+5 1.6 E+9 2.6 E+5 1.6 E+9 1.9 E+5 1.6 E+9 Cs - 136 3.1 E4 3.4 E+7 3.4 E+4 3.4 E+7 4.4 E4 3.4 E+7 3.3 E A 3.4 E+7 Cs - 137 1.4 E+5 2.3 E+9 1.9 E+5 2.3 E+9 1.9 E+5 2.3 E 9 1.4 E+5 2.3 E+9 Eh - 140 1.3 E 4 4.7 E+6 1.7 E 4 4.7 E+6 5.2 E44 4.7 E4 5.0 E4 4.7 E4 Ce - 141 4.9 E+3 3.1 E+6 1.3 E4 3.1 E+6 2.9 E*4 3.1 E+6 2.7 E44 3.1 E+6 Ce - 144 3.4 E4 1.6 E+7 8.9 E+4 1.0 E+7 2.0 E+5 1.6 E+7 1.9 E+5 1.6 E+7 I - 131 3.4 E+6 3.9 E4 3.7 E4 3.9 E4 3.3 E4 3.9 E-5 2.7 E4 3.9 E4 I - 133 5.1 E+5 5.' E-5 5.8 E+5 5.6 E4 6.7 E+5 5.6 E-5 4.9 E-5 5.6 E4 I - 135 1.6 E+5 5.5 E+5 1.8 E+5 5.8 E6 1.4 E+5 5.5 E4 1.0 E+5 5.5 E+5 11dentified 9.3 E+6 0 2.3 E+7 0 2.7 E+7 0 2.3 E+7 0 trevyr *:8 - mm/yr yCUk vCi/sec 2~2 Rev. 8 7-1-82
Page 2 of 3 7ABiI 2-5 Dose Parameter Ri for M Sector Pathay Nearest Residence Distance 2.8 miles X4 2.T-7 D4 3. AE-10 Infant 0111d Teen Adult Radimtelide Inhalatim Food & Gromd Inhalatim Food & Gnxvid Inhalatim Food & Grtmi Inhalation Food & Gromd
'Pathay "Pathay Pathay Pathcy Pathay Pathey Pathay Pathay H- 3 6.5 E+2 5.1 E+3 3.9 E+3 3.6 E+3 P - 32 2.0 E+6 0 2.6 E+6 3 3 E+9 1.9 E+6 1.8 E+9 1.3 E+6 1.5 E+9 Cr - 51 3.6 E+2 4.7 E+6 1.1 E+3 1.1 E+7 3 0 E+3 1.5 E+7 3 3 E+3 1.6 E+7 M1 - 5'4 2.5 E 4 1.4 E+9 4.3 E4 2.0 E+9 6.7 E 4 2.3 E+9 7.7 E 4 2.3 E+9 FJ - 59 2.4 E4 2.7 E+8 3.3 E4 9.0 E+8 1.8 E+5 1.2 E+9 1.9 E45 1.2 E+9 Co - 58 1.1 E4 3.8 E+8 3.4 E4 7.5 E+8 9.5 E 4 9.7 E+8 1.1 E+5 9 9 E+8 Co - 60 3 2 E+4 2.2 E+10 9.6 E4 2.4 E+10 2.6 E+5 2.5 E+10 2.8 E45 2.5 E+10 Zn - 65 6.3 E 4 7.5 E+8 1.1 E+5 3.5 E 4 1.3 E+5 2.6 E+9 1.0 E+5 2.0 E+9 Rb - 86 1.9 E+5 9.0 E46 2.0 E45 4.7 E+8 1.9 E+5 2.9 E+8 1.4 E+5 2.3 E48 Sr - 89 4.0 E+5 2.2 E+4 6.0 E+5 3.5 E+10 4.3 E+5 1.5 E.10 3.0 E+5 9.8 E+9 Sr - 90 4.1 E+7 0 1.0 E+8 1.4 E+12 1.1 E+8 8.3 E+11 9.9 E+7 6.7 E+11 Y- 91 7.0 E+4 1.1 E+6 1.8 E+5 2.4 E+9 4.1 E+5 3.1 E+9 3.8 E+5 2.8 E+9 Zr - 95 2.2 E+4 2.5 E+8 6.1 E44 1.1 E+9 1.5 E+5 1.5 E+9 1.5 E+5 1.4 E49 lb - 95 1.3 E 4 1.u E+8 3.7 E4 4 3 E+8 9.7 E4 5.9 E+8 1.0 E+5 6.1 E+8 Ru - 103 1.6 E4 1.1 E+8 4.5 E4 5.0 E+8 1.1 E45 6.8 E.8 1.1 E+5 6.6 E+8 Ru - 106 1.6 E+5 4.2 E+8 4.3 E+5 1.2 E+10 9.6 E+5 1.5 E+10 9.1 E+5 1.3 E+10 Ag - 11 m 3 3 E4 3.5 E+9 1.0 E+5 6.6 E+9 2.7 E+5 7.1 E+9 30 E+5 9 8 E+9 Cd - 1194 7.0 E+4 0 1.8 E+5 2.0 E+9 4.1 E+5 2.6 E+9 3.8 E+5 2 3 E+9 Sn - 123 2.9 E+5 0 u.8 E+5 6.3 E+9 3 3 E-5 4.0 E-9 3.1 E45 34 E+9 Sn - 126 1.2 E+6 2.f E+" 2.3 E+6 3.0 E+$0 1.7 E4 3.6 I+10 1.3 E+6 3.3 E+'0
.1 - 124 5.9 Eu f." I+i 1.6 E45 2.9 E4 L.? E+5 3.6 E4 4.1 E+5 3.5 E4 Sb - 125 1.5 E d 2. E4 4.0 E+4 3.5 E+9 9.9 E 4 3.9 E+9 1.0 E+5 3.8 E+9 Te - 12'N 3.8 E4 9.2 E+L 6.4 E4 5.3 E+9 6.5 E4 3.2 I+9 4.6 E4 2.0 E4 T2 - 1291 3.2 E4 2.0 E+7 5.0 E+4 2.9 E+9 5.2 E 4 1.8 E+9 37 E4 1.2 E+9 Cs - 134 7.0 E45 6.8 E+9 1.0 E46 3.3 E+10 1.1 E46 2.3 E+10 8.5 E+5 1.8 E+10 Cs - 136 1.3 E+5 1.5 E+8 1.7 E+5 3.8 E+8 1.9 E+5 3.2 E+8 1.5 E+5 3.2 E+8 Cs - 137 6.1 E+5 1.0 E+10 8.3 E45 3.4 E+10 8.5 E+5 2.4 E+10 6.2 E+5 1.9 E+10 Ib - 140 5.6 E4 2.1 E+7 7.4 E4 3.0 E+8 2.3 E+5 2.3 E+8 2.2 E+5 2.9 E+8 Ce - 141 2.2 E4 1. :. E+7 5.7 E44 4.7 E+3 1.3 E45 5.5 E-8 1.2 E+5 5.2 E-8 Ce - 144 1.5 E+5 7.0 E+7 3.9 E+5 1.0 E+10 8.1 E+5 1.3 E+10 8.2 E+5 1.1 E+10 I - 131 1.7 E+7 1.' E+' 1.6 E+7 4.8 E+10 1.5 E+7 3.1 E+10 1.2 E+7 3.8 E+10 I - 133 3.6 E+6 2.- I+( 3.8 E+6 8.1 E+e 0.9 E*6 L.6 E+8 2.2 E+6 5.3 I+5 I - 135 7.0 E+5 2.5 E 6 7.9 E+5 1.2 E.7 6.2 E+5 s.2 E-6 4.5 E+5 1.* E-6 i
Unidentified 4.1 E+7 0 1.0 E+8 1.4 E+12 1.1 E+8 8.3 I+11 9.9 E+7 6.7 E+11 arrevy- a r2 _ ,,yyr uCi/h pC1/sec 2-25 h*l
- 8h
Page 3 of 3 TA!I.I 2-5 Dose Parawte- R1 for M Sector Pathay Milk Pathay Distance 4.5 miles XA] 6.1E-8 DA) 1.2 E-10 Infant 0111d Test Adult Ladiernr.lide Inhalatim Food & Grurd Inhalatim Food & Grumd Inhalatim Ford & Grusd Inhalatim Food & Gromd
'Pathay **Pathay Pathey Pathay Pathay Pathey Fathay Pathway H -
3 0 2.4 E+3 0 1.6 E+3 0 9.9 E+2 0 7.6 E+20 P -
32 0 1.6 E+11 0 7.6 E+10 0 3.1 E+10 0 1.'r E+10 Cr - 51 0 4.2 E+6 0 4.8 E 6 0 7.5 E46 0 6.4 E+6 Mn - 54 0 3.1 E+7 0 1.7 E+7 0 2.3 E+7 0 2.1 E+7 F2 - 59 0 3.4 E+8 0 1.7 E+8 0 2.5 E 8 0 2.0 E+8 Co- 38 0 5.0 E+7 0 5.9 E+7 0 9.1 E+7 0 7.9 E+7 Co - 60 0 1.7 E+8 0 1.9 E+8 0 2.9 E.8 0 2.4 E+8 Zn - 65 0 1.7 E+10 0 9.9 E+9 0 6.6 E+9 0 3.9 E+9 Rb - 86 0 2.1 E+10 0 8.2 E+9 0 4.4 E+9 0 2.4 E+9 Sr - 89 0 1.1 E+10 0 5.6 E+9 0 2.3 E+9 0 1.2 E+9 Sr - 90 0 1.0 E+11 0 9.3 E+10 0 5.5 E+10 0 3.9 E+10 Y - 91 0 4.4 E+6 0 4.u E+6 0 5.4 E+6 0 4.0 I+6 Zr - 95 0 6.9 E+5 0 7.4 E+3 0 1.0 E+6 0 8.0 E.5 Nb - 95 0 1.8 E+8 0 2.0 E+8 0 2.9 E+8 0 2.4 E+8 Ru - 103 0 9.2 E 4 0 9.6 E+4 0 1.3 E+5 0 1.0 E+5 fu - 106 0 1.2 E+6 0 1.2 E+6 0 1.4 E+6 0 1.1 I+6 Ag - 11CM 0 1.2 E+10 0 1.6 E+10 0 2.1 E+10 0 1.5 E+10 Cd - 1194 0 5." E+7 0 5.1 E+7 0 6.4 E+7 0 4.6 E+7
.% - 123 C 3.' E+0 0 2.~ E4 C '2 E4
. 0 S.E I4 Sn - 1 6 0 . ;E3 0 5.e E.9 R 2.3 E.; O 1.3 E.9 Sb - 124 0 5.; E+B o 5.7 E48 0 7.8 E+3 0 6.1 E48
.% - 123 0 1.5 E+8 0 1.6 E+8 0 2.2 E+8 0 1.6 E+8 Ta - 127M 0 1.0 E+9 0 5.8 E 8 0 3.3 E+8 0 1.8 E+8 Ta - 1294 0 1.3 E+9 0 7.5 E+8 0 4.3 E+8 0 2.1 E+8 Cs - 134 0 5.4 E+10 0 2.9 E+10 0 1.8 E+10 0 1.1 E+10 Cs - 136 0 5.5 E+9 0 2.6 E+9 0 1.7 E+9 0 9.9 E+8 Ca - 137 0 1:.9 E+10 0 2.5 E+10 0 1.4 E+10 0 8.1 E+9 Ib - 140 0 2.3 E+8 0 1.1 E+8 0 7.2 E+7 0 5.3 E+7 Ce - 141 0 1.2 E+7 0 1.2 E+7 0 1.5 E+7 0 1.1 E+7 Ce - 144 0 1.' E.8 0 1.^ E.8 0 1.3 E+8 0 9.6 E+7 I - 13' ~
".' E.~i 0 1. 3 E+ * : 2.2 E+ 1 0 1.L E" I - 133 C 5.6 E+9 0 3.9 E.9 0 1.7 E+9 0 9.9 E+E I - 135 0 2.0 E+7 0 8.5 E4 0 3.7 E+6 0 2.2 E+6
, identified 0 1.0 E+11 0 9.3 E+10 0 5.5 E+10 0 3.9 E+10
':TeVyr r2 - :reVyr pC1/M pCi/see I~
Rev. 8 7-1-82
Page 1 of 4 TAB;I 2-6 Ibse Para, eta R 1 for !M Sector Pathey Fanily Housirs Distance 1.8 miles X4 7.1E-7 DS 2.2 E-9 Infant 0111d Tem k! ult Mionuclide Inhalatim Food & Ground Inhalatim Food & Gromd Inhalatim Food & Grurd Inhalatim Food & Grund
'Pathay "Pathay Pathay Pathey Pathay Pathey Pathay Pathey H- 3 6.5 E42 0 5.1 E+3 0 3 9 E+3 0 3.6 E+3 0 P -
32 2.0 E+6 0 2.6 E+6 3.3 E+7 1.9 E+6 1.8 E+4 1.3 E+6 1.5 E+9 Cr - 51 3.6 E42 4.7 E+6 1.1 E+3 1.1 E+7 3.0 E+3 1.5 E+7 3.3 E+3 1.6 E+7
!+1 - 54 2.5 E*4 1.4 E+9 4.3 E4 2.6 E+9 6.7 E 4 2.3 E+9 7.7 E 4 2.3 E+9 F1 - 59 2.4 E4 2.7 E+8 3.3 E4 9.0 E+8 1.8 E+5 1.2 E+9 1.9 E45 1.2 E+9 Co - 58 1.1 E4 3 8 E+8 34 E4 7.5 E+8 9.5 E4 9.7 E+8 1.1 E+5 9.9 E+8 Co - 60 3 2 E4 2.2 E+10 9.6 E4 2.4 E+10 2.6 E+9 2.5 E+10 2.8 E+5 2.5 E+10 Zn - 65 6.3 E 4 7.5 E+8 1.1 E+5 3.5 E+4 1.3 E+8 2.6 E+9 1.0 E+5 2.0 E+9 Rb - 86 1.9 E*5 9.0 E+6 2.0 E+5 4.7 E+8 1.9 E45 2.9 E+8 1.4 E45 2.3 E48 3- 19 4.0 E+5 2.2 E+4 6.0 E+5 3.5 E+10 4.3 E+5 1.5 E+10 3.0 E+5 9.8 E+9 Sr - 90 4.1 E+7 0 1.0 E+8 1.4 E+12 1.1 E+8 8.3 E+11 9.9 E+7 6.7 E+11 Y- 91 7.0 E4 1.1 E+6 1.8 E+5 2.4 E+9 4.1 E+5 31 E+9 3.8 E+5 2.8 E+9 Zr - 45 2.2 E44 2.5 E+8 6.1 E+4 1.1 E+9 1.5 E45 1.5 E49 1.5 E+5 1.4 E+9 Nb - 95 1.3 E 4 1.4 E+8 3.7 E+4 4.3 E+8 9.7 E 4 5.9 E+8 1.0 E+5 6.1 E.8 Ru - 103 1.6 E4 1.1 E+8 4.5 E4 5.0 E+8 1.1 E+5 6.8 E+8 1.1 E+5 6.6 E+8 RJ - 106 1.6 E+5 4.2 E+8 4.3 E+5 1.2 E+10 9.6 E+5 1.5 E+10 9.1 E+5 1.3 E+10 A6 - 1104 3.3 EA 3.5 E+9 1.0 E+5 6.6 E+9 2.7 E+5 7.1 E49 3.0 E45 7.8 E+9 Cd - 1194 7.0 E+4 0 1.8 E+5 2.0 E+9 4.1 E+5 2.6 E+9 3.8 E+5 2.3 E+9 31 - 123 2.9 E+5 0 4.8 E+5 6.3 E+9 3 3 E+5 4.0 E+9 31 E45 3.4 E+9 Sn - 126 1.2 E+6 2.6 E+10 2.3 E+6 5.0 E+10 1.7 E+6 3.6 E+10 1.3 E+6 3.3 E+10 St "24 5.9 E+4 6.0 E+: 1.6 E+5 2.5 E+0 4.0 E+5 3.6 E+9 4.1 E+5 35 E+9 St:- 125 1.5 E+4 2.3 E+9 4.0 E :- 3.5 E-9 9.9 E 4 3.9 E+4 1.0 E+5 3.5 E+)
Ta - 1234 3. 3 E4 9.2 E4 6.4 E4 5.4 E+9 6.5 E4 3.2 E+4 4.6 E4 2.C E+9 Te - 1234 3.2 Ew 2.0 E+7 5.0 E+4 2.9 E+9 5.2 E4 1.8 E+9 3.7 E 4 1.2 I+9 Cs - 134 7.0 E45 6.1 E+9 1.0 E+6 3.3 E+10 1.1 E46 2.3 E+10 8.5 E45 1.8 E+10 Cs - 136 1.3 E+5 1.5 E+8 1.7 E+5 3.8 E+8 1.9 E+5 3.2 E+8 1.5 E+5 3 2 I+8 Cs - 137 6.1 E+5 1.0 E+10 8.3 E+5 3.4 E+10 8.5 E+5 2.4 E+10 6.2 E45 1.9 E+10 Ba - 140 5.6 E4 2.1 E+7 7.4 E4 3.0 E+8 2.3 E+5 2.3 E+8 2.2 E+5 2.9 E+8 Ce - 141 2.2 E4 1.4 E+7 5.9 E4 4.7 E+8 1.3 E+5 5.5 E+8 1.2 E+5 5.2 E.8 Ce - 144 1.5 E+5 7.0 E+7 3.9 E+5 1.0 E+10 8.6 E+5 1.3 E+10 8.2 E+5 1.1 E+10 I - 131 1.7 E+7 1.7 E+7 1.6 E+7 4.S E+10 1.5 E+7 3.1 E+10 1.2 E+7 3.8 E+10 I - 133 3.6 E+6 2.u E+6 3.8 E*6 E.1 E+e 8.9 E+6 4.6 E+8 2.2 E+6 5.3 I+8
- - 935 ~. n E5 2.5 E+6 7.9 E+5 ".2 E' 6.2 E+5 E.2 E/. 4.5 E+5 1.* E4
. identified 4.1 E+7 0 1.0 E+8 1.4 E+12 1.1 E+8 E.3 E+11 9.9 E+7 6.~ E+1' Nren/yr '+c2 - crm/yr 2
p C1/f pCi/sec 2-27 a N*-82
l Page 2 of 4 7ABLE 2-6 Ibse Parameta R 1 for !W Sector Path ey Vegetable Card e Dis +mce 2.2 miles X4 4.6 E 7 D4 1.3 E4 Infant 0111d Tem Adult
'adionuclide Inhalation Food & Omsd Inhalatim Food & Gerd Inhalatim Food & Gmsd Inhalatim Food & Gromd
- Pathay **Pathay Pathay Pathay Pathay Pathway Pathay Pathay H- 3 1.6 E 4 0 2.9 E+3 2.6 E+3 P- 32 5.1 E+5 0 6.5 E+5 3.7 E+9 4.7 E+5 1.8 E+9 3.3 E+5 1.5 E+9 Cr - 51 1.2 E+6 7.3 E46 7.5 E.2 1.1 E+7 8 3 E+2 1.7 E+7 m - 54 6.3 E+3 3.5 E+8 1.1 E+4 1.0 E+9 1.7 E4 1 3 E+9 1.9 E 4 1.3 E+9 F1 - 59 5.9 E+3 6.8 E+7 8.4 E+3 2.0 E+8 4.5 E4 1.0 E+9 4.7 E44 1.0 E+9 Co - 58 2.8 E+3 9.5 E+7 8.6 E+3 4.6 E+8 2.4 E+4 6.8 E+8 2.7 E 4 7.0 E+8 Co - 60 8.0 E+3 5.4 E+9 2.4 E4 7.5 E+9 6.5 E4 8.6 E+9 7.1 E4 8.5 E+9 2n - 65 1.6 E 4 1.9 E+8 2.8 E 4 2.9 E+9 3.3 E 4 2.1 E+9 2.6 E+4 1.5 E+9 Hb - 86 4.8 E+4 2.3 E 6 5.0 E4 4.6 E+8 4.8 E4 1.8 E.8 3.4 E4 2.2 E.8 3r - 89 9.9 E 4 5.4 E+3 1.5 E+5 3 5 E+10 1.1 E+5 1.5 E+10 2.6 E+4 9.8 E+9 3r - 90 1.0 E+7 0 2.5 E+7 1.4 E+12 2.7 E+7 8.3 E+11 2.5 E+7 6.7 E+11 Y- 91 1.8 E 4 2.7 E+5 4.6 E+4 2.4 E+9 1.0 E+5 3.1 E+9 9.6 E4 2.8 E+9 Zr - 95 5.4 E+3 6.3 E+7 1.5 E4 9.4 E+6 3.7 E44 1.3 E+9 3.8 E4 1.3 E49 tb - 95 3.2 E+3 3.4 E+7 9.2 E+3 3.3 E+8 2.4 E4 4.8 E+8 2.6 E+4 5.1 E+8 RJ - 103 4.0 E+3 2.7 E+7 1.1 E+4 4.2 E48 2.7 E4 5.9 E+8 2.8 E4 5.8 E+8 RJ - 106 4.1 E4 1.1 E+8 1.1 E+5 1.2 E+10 2.4 E+5 1.5 E+10 2.3 E+5 1.3 E+10 Ag - 11CE 8.3 E+3 8.7 E+8 2.5 E4 4.0 E+9 6.8 E4 5.2 E49 7.6 E44 5.2 E+9 Cd - 1191 1.8 E+4 0 4.6 E4 2.0 E+9 1.0 E+5 2.6 E+9 9.6 E4 2.3 E+9
& - 123 7.4 E+4 0 1.2 E+5 6.3 E L S.3 E+4 4.0 E+9 7.8 E4 3.4 E49
& - 126 2.9 E+5 6.5 E+9 5.9 E+5 3.' E+i" 4.4 E+5 1.' Ev0 3.2 E+5 1.3 E+'~
Tc - 124 1.5 E-~ 1.5 E-E L.1 E" 2 3 E4 1.0 E-5 3 2 E+9 '." E+5 3. ~ E 3 Sb - 125 3.7 E+3 5.8 E+8 1.0 E 4 1.8 E+9 2.5 E 4 2.2 E+9 2.5 E+4 2.1 E+9 Te - 127M 9.4 E+3 2.3 E4 1.6 E4 5.4 E+: 1.6 E4 3.2 E+9 1.1 E4 2.C E4 72 - 129M 7.9 E+3 4.9 E+6 13E4 2.9 E+9 1.3 E 4 1.6 E+9 9.1 E+3 1.2 E+9 Cr - 134 1.8 E 5 1.7 E.9 2.5 E+5 2.7 E+10 2.8 E.5 1.8 E+10 2.1 E5 1.3 E+10 Cs - 136 3.4 E+4 3.8 E+7 4.3 E 4 2.6 E+8 4.8 E 4 2.1 E+8 3.7 E 4 2.1 E+8 Cs - 137 1.5 E+5 2.6 E+9 2.1 E+5 2.7 E+10 2.1 E45 1.7 E+10 1.6 E+5 1.2 E+10 Ib - 140 1.4 E+4 5.1 E+6 1.9 E4 2.8 E+8 5.7 E 4 2.2 E+8 5.5 E4 2.7 E+8 Ce - 141 5.4 E+3 34 E+6 1.4 E4 4.1 E+8 32 E4 5.4 E+8 3.0 E4' 5.1 E+8 Ce - 144 3.7 E4 1.2 E+7 9.7 E4 1.0 E+10 2.2 E+5 1.3 E+10 2.0 E+5 1.1 E+10 I - 131 3 7 E+6 4.3 E4 4.1 E46 L.9 E45 3.7 E+6 31 E+10 30 E+6 3.8 E+10
- - 133 5.9 E+5 5.1 E5 S.6 E-5 E.1 E+E 7.3 E+5 4.6 E+8 5.L E+5 5.3 E+i I - 135 6.3 E 5 ." E+T 1.6 E+5 6.- E+4 *1. E+5 7.2 E-6 hidentified 1.0 E+17 0 2.5 E+~ 1.4 E+12 2.7 E+7 8.3 E4 2.5 E+7 6.7 E+11
%revyr **r8 - nrevyr 2
pCLM pCi/sec
-0 !!ev. 8 7-1-82
Page 3 of 4 TAKI 2-6 tbse Para ete- R$ for y Sector Pahey Meat (Cattle) Patbey Distance 4.0 miles X4 1.4 E-7 D4 3.4 E-10 Infant 0111d Teen Mult Radimuclide Inhalatim Food & Grourd Inhalatim Food & Gnxrd Inhalatim Food & Grurd Inhalatim Food & Grusd
'Pathay "Pathay Pathay Pathey Pathay Pathway Pathey rathay H- 3 3 2 E+1 0 2.9 E+2 0 2.5 E+2 0 3 8 E42 0 P - 32 1.0 E+5 0 1.3 E+5 7.3 E+9 9.4 E4 3.9 E+9 6.6 E+4 4.6 E+9 Cr - 51 1.8 E+1 2.3 E45 5.4 E+1 6.5 E+5 1.5 E+2 1.1 E+6 1.7 E42 1.8 E 6 Hi - 54 1.3 E+3 6.9 E+7 2.1 E+3 7.6 E+7 3.3 E+3 8.1 E+7 3.9 E+3 9.2 E+7 Fa - 59 1.2 E+3 1.1 E+7 1.7 E+3 5.4 E+8 8.9 E+3 1.0 E+9 9.4 E+3 1.8 E 9 Co - 58 5.6 E+2 1.9 E+7 1.7 E+3 9.9 E+7 4.8 E+3 1.8 E+8 5.3 E+3 3.3 E+8 Co - 60 1.6 E+3 1.1 E+9 4.8 E+3 1.4 E+9 1.3 E4 1.7 E+9 1.4 E4 2.2 E+9 Zn - 65 3.1 E+3 3.7 E+7 5.7 E+3 9.4 E+8 6.7 E+3 8.2 E+8 5.2 E+3 1.1 E+9 Pb - 86 9.5 E+3 4.5 E+5 9.9 E+3 5.4 E+8 9.5 E+3 3.8 E+8 6.8 E+3 4.6 E+8 Sr - 89 2.0 E+4 1.1 E+3 3.0 E+3 4.1 E+8 2.2 E 4 2.2 E+8 1.5 E4 2.6 E+8 Sr - 90 2.0 E 6 0 5.1 E+6 8.6 E+4 5.4 E+6 6.7 E+9 5.0 E+6 1.0 E+10 Y -
91 3.5 E+3 5.4 E+4 9.2 E+3 2.0 E+8 2.0 E 4 3.3 E+8 1.9 E 4 5.2 E+8 Z.' - 95 1.1 E+3 1.3 E+7 3.1 E+3 5.5 E+8 7.4 E+3 9.3 E+8 7.5 E+3 1.6 E+9 Nb - 95 6.3 E42 6.8 E+6 1.8 E+3 2.0 E+9 4.8 E+3 3.7 E+9 5.2 E+3 6.8 E+9 Ru - 103 8.0 E+2 5.4 E46 2.2 E+3 3.5 E+9 5.4 E+3 6.2 E+9 5.5 E+3 1.1 E+10 Ra - 106 8.2 E+3 2.1 E+7 2.1 E44 5.6 E+10 4.8 E+4 9.1 E+10 4.6 E+4 1.5 E+11 Ag - 11m 1.7 E+3 1.7 E+8 5.0 E+3 8.1 E+8 1.4 E4 1.3 E+9 1.5 E4 2.3 E 9 Cd - 115M 3.5 E+3 0 9.2 E+3 2.1 E+7 2.0 E+4 3.5 E+7 1.9 E+4 5.3 E+7
& - 123 1.5 Ea 0 2.4 E4 7.1 E+9 1.7 E4 5.7 E+9 1.6 E4 4.1 E+9 En - 126 5.8 E+4 1.3 E+9 1.2 E-5 2 3 E+10 8.7 Ea 1.3 E+10 6.3 E 4 .6 E+13 Sb - 124 3.0 E+3 3.0 E+~ 8.2 E-3 ' 5 E-?
. 8.0 E4 3.0 E+5 2.0 E+4 5." E-3 Sb - 125 7.3 E+2 1.2 E+8 2.0 E+3 1.7 E+8 5.0 E+3 2.1 E+8 5.0 E+3 2.8 E+8 Ta - 12iH 1.9 E+3 4.6 E+3 3 2 E+3 5.0 E+9 3.3 E+3 3.7 E+9 2.3 E+3 4.4 E+9 Te - 129M 1.6 E+3 9.8 E+5 2.5 E+3 4.9 E+9 2.6 E+3 3.7 E+9 1.8 E+3 4.5 E+9 Cs - 134 3.5 E4 34 E+8 5.1 E4 1.5 E+9 5.6 E4 1.3 E+9 4.2 E4 1.6 E 9 Cs - 136 6.7 E+3 7.5 E+6 8.5 E+3 5.0 E+7 9.7 E+3 4.3 E+7 7.3 E+3 5.3 E+7 Cs - 137 3.1 E4 5.1 E8 4.1 E4 1.6 E 9 4.2 E4 1.3 E+9 31 E4 1.5 E+9 h - 140 2.8 E+3 1.0 E46 3.7 E+3 4.3 E+7 1.1 E4 3.6 E+7 1.1 E+4 3.8 E+7 Ce - 141 1.1 E+3 6.8 E+5 2.8 E+3 1.3 E+7 6.3 E+3 2.1 E+7 6.0 E+3 3. 3 E+7 Ce - 144 2.4 E+3 3 5 E+6 1.9 E a 1.5 E+8 4.3 E 4 2.5 E+8 4.1 E+4 3.9 E+8 I - 1 31 7.4 E+5 8.6 E+5 8.1 E+5 5.4 E+9 2. 3 E+5 3.6 E+9 6.0 E+5 5.0 E+9 I 133 1.S E+5 1.2 E+5 1.9 E-5 .2 E+5 1.5 E+5 1.2 E+5 1.1 E+5 1.2 E-5 1 - 135 3.5 L+4 1.3 E4 4.E E- ' 3 E+5
. 3.1 E+4 1.3 E+5 2.2 E- " 3 E+5 Jnidentified 2.0 E+6 0 5.1 E+6 8.6 E+9 5.6 E+6 6.7 E+9 5.0 E+6 1.0 E+13
'r:reVyr **:8 - rrm'y-pCi/h t.Ci/sec 2- 9 Rev. 8 7-1-82 L
Page 4 or 4 TAKE 2-6 Ibse Pa-awter R1 forIM, Sector Patt.way Milk Pathey Distance 4.5 miles X4 8.5 E-8 DC 2.6 E-10 Infant O'.ild Teen Adult
. Ratianuclide Inhalatim Food & Ommd Inhalatim Food & Grtmd Inhalatim Food & Gromd Inhalation Food & Grted
' Path ey **Pathay Fathay Pathay Pathey Pathay Pathay Pathay H -
3 0 2.4 E+3 0 1.6 E+3 0 9.9 E4 0 7.6 E420 P -
32 0 1.6 E+11 0 7.6 E+10 0 3.1 E+10 0 1.7 E+10 Cr - 51 0 4.2 E+6 0 4.8 E+6 0 7.5 E*6 0 6.4 E+6 tti - 54 0 3.1 E4 0 1.7 E+7 0 2.3 E+7 0 2.1 E4 F2 - 59 0 3.4 E8 0 1.7 E+8 0 2.5 E+8 0 2.0 E+8 Co - 58 0 5.0 E+7 0 5.9 E+7 0 9.1 E4 0 7.9 E+7 Co - 60 0 1.7 E+8 0 1.9 E 8 0 2.9 E+8 0 2.4 E+8 Zn - 65 0 1.7 E+10 0 9.9 E4 0 6.6 E+9 0 3.9 E+9 Ib - 86 0 2.1 E+iG 0 8.2 E+9 0 4.4 E+9 0 2.4 E49
&- 89 0 1.1 E+10 0 5.6 E+9 0 2.3 E+9 0 1.2 E+9 Sr - 90 0 1.0 E+11 0 9.3 E+10 0 5.5 E+10 0 3.9 E+10 Y -
91 0 4.4 E+6 0 4.4 E+6 0 5.4 E+6 0 4.0 E+6 Zr - 95 0 6.9 E+5 0 7.4 E+5 0 1.0 E+6 0 8.0 E+5 tb - 95 0 1.9 E+8 0 2.0 E.8 0 2.9 I+8 0 2.4 E+8 Ru - 103 0 9.2 E+4 0 9.6 E44 0 1.3 E*5 0 1.0 E45 lb - 106 0 1.2 I+6 0 1.2 E+6 0 1.4 E.6 0 1.1 E+6 Ag - 11CN 0 1.2 E+10 0 1.6 E+10 0 2.1 E+10 0 1 3 E+10 Cd - 11 T 0 5.7 E+7 0 5.1 I+7 0 6.4 E4 0 4.6 E4 Sn - 123 0 3.7 E+9 0 2.0 E+9 0 1.2 E+9 0 8.5 E+6 Sn - 126 0 3.9 E4 0 5.a E.? O 2 3 I+0 0
- 3 I+9 c - 12* 0 5.- E-5 0 5.7 E-3 0 .i E-i 0 C.* E+i Sb - 125 0 1.6 E.8 0 1.6 E.8 0 2.2 I+8 0 1.5 E+8 Te - 127M 0 1.0 E+9 0 5.8 E46 0 3.3 E+S 0 1.5 E+S T2 - 129M 0 1.3 E+9 0 7.5 E+8 0 4.3 E+8 0 2.3 E+8 Cs - 134 0 5.4 E+10 0 2.9 E+10 0 1.8 E+10 0 1.1 E+10 Ca - 136 0 5.5 E+9 0 2.6 I+9 0 1.7 I+9 0 9.9 E4 cs - 137 0 4.9 E+10 0 2.5 E+10 0 1.u E+10 0 8.1 E+9 Ba - 140 0 2.3 E+8 0 1.1 E+8 0 7.2 E4 0 5.3 E+7 Ce - 141 0 * ? E+7
. 0 1.2 E+7 0 1.5 E+ 7 0 1.1 E+7 Ce - 144 0 1.1 E+6 0 1.0 I+8 0 1.3 E+8 0 9.6 E 4 I - 131 0 1.0 E+12 0 4.3 E+'l 0 2.2 E+11 0 1.L E+11 I - '33 0 9.6 E.9 0 3.9 E-; o .- E+9 0 9.; E.5 I - 135 0 2.0 E.7 0 d.5 L /. 0 3. E4 0 2.2 I+5
. Unidentified 0 1.0 E+11 0 9.3 E+10 0 5.5 E+10 0 3.9 E+10 8:Te ./y- M - nrevyr 1
pCi/W uCi/sec 2-30 Rev. 8 7-1-82
Page 1 of 4 TAKI 2-7 Dose Pa-awtAr Ri for ?J{%' Sectcr Pathay !ttile Haies Dis +w re 1.3 miles X4 1.8 E-6 DN 8.8 E-9 Infant 0111d Teel Mult
%dionuclide Inhalatim Food & Grourd Inhalatim Food & Gromd Inhalation Food & Gromd Inhalatim Food & Grourd
'Pathey **Pathay Pahy Pathay Pathey Pathey Pathay Pathey H - 3 6.5 E+2 0 5.1 E+3 0 3.9 E+3 0 3.6 E+3 0 P- 32 2.0 E+6 0 2.6 E+6 3 9 E+9 1.9 E+6 1.8 E+9 1.3 E46 1.5 E+9 Cr - 51 3.6 E42 4.7 E+6 1.1 E+3 1.1 E+7 3.0 E+3 1.5 E+7 3.3 E+3 1.6 E+7 th - 54 2.5 E 4 1.4 E+9 4.3 E+4 2.0 E+9 6.7 E4 2.3 E+9 7.7 E+4 2.3 E+9 F2 - 59 2.4 E4 2.7 E*8 3.3 E4 9.0 E+8 1.8 E*5 1.2 E+9 1.9 E+5 1.2 E 9 Co - 58 1.1 E+4 3.8 E+8 34 E+4 7.5 E+8 9.5 E 4 9.7 E+8 1.1 E+5 9.9 E+8 Co - 60 3.2 E4 2.2 E+10 9.6 E+4 2.4 E+10 2.6 E+5 2.5 E+10 2.8 E+5 2.5 E+10 In - 65 6.3 E4 7.5 E+8 1.1 E+5 3 5 E4 1.3 E+5 2.6 E+9 1.0 E+5 2.0 E+9 Hb - 86 1.9 E45 9.0 E.6 2.0 E+5 4.7 E+8 1.9 E*5 2.9 E*8 1.4 E+5 2.3 E+8 Sr - 89 4.0 E+5 2.2 E4 6.0 E+5 3.5 E+10 4.3 E+5 1.5 E+10 3.0 E+5 9.8 E+9 Sr - 90 4.1 E+7 C 1.0 E+8 1.4 E+12 1.1 E+8 8.3 E+11 9.9 E+7 6.7 E+11 Y- 91 7.0 E 4 1.1 E+6 1.8 E+5 2.4 E+9 4.1 E+5 3.1 E+9 3.8 E+5 2.8 E+9 Zr - 95 2.2 E4 2.5 E4 6.1 E+4 1.1 E4 1.5 E+5 1.5 E.9 1.5 E+5 1.4 E*9 tb - 95 1.3 E 4 1.4 E+8 3.7 E 4 4.3 E+8 9.7 E+4 5.9 E.8 1.0 E+5 6.1 E4 Ru - 103 1.6 E4 1.1 E+8 4.5 E4 5.0 E+8 1.1 E+5 6.8 E+3 1.1 E+5 6.6 E+8 lb - 106 1.6 E+5 4.2 E+8 4.3 E+5 1.2 E+10 9.6 E+5 1.5 E+10 9.1 E+5 1.3 E+10 Ag - 110M 3.3 E+4 3.5 E+9 1.0 E+5 6.6 E4 2.7 E+5 7.1 E4 3 0 E+5 7.8 E4 Cd - 1194 7.0 E4 0 1.8 E+5 2.0 E+9 4.1 E+5 2.6 E+9 3.8 E+5 2.3 E+9 Sn - 123 2.9 E+5 0 4.8 E.5 6.3 E4 3.3 E+5 4.0 E : 31 E+5 34 E+9 Sn - 126 1.2 E+6 2.5 E+10 2.3 E+6 30 E+1: 1.7 I+6 3.6 I+7 1.3 E+6 3.3 E+10 1 - 12, 5.9 E4 (.- E4 1.6 E+5 2.5 E4 c.0 E45 3.6 E4 a.1 E+5 3.5 E.9 Sb - 13 1.5 E 4 2.3 E+9 4.0 E4 3.5 E+9 9.9 E 4 3.9 E4 1.0 E+5 3.8 E+9 70 - 12?M 3.8 E4 9.2 E+:- 6.4 E4 5.4 E+9 6.5 E+4 3.2 E.9 4.6 E4 2.0 E+9 T2 - 129H 32 E4 2.0 E+7 5.0 E4 2.9 E+9 5.2 E4 1.8 E+9 3.7 E+4 1.2 E+9 cs - 134 7.0 E+5 6.8 E4 1.0 E46 3.3 E+10 1.1 E46 2.3 E+10 8.5 E45 1.8 E+10 cs - 136 1.3 E+5 1.5 E+8 1.7 E+5 3.8 E+8 1.9 E+5 3.2 E4 1.5 E+5 3.2 E+8 Cs - 137 6.1 E+5 1.0 E+10 8.3 E45 3.4 E+10 8.5 E*5 2.4 E+10 6.2 E+5 1.9 E+10 Ba - 140 5.6 E4 2.1 E+7 7.4 E4 30 E+8 2.3 E+5 2 3 E+8 2.2 E+5 2.4 E+8 Ce - 141 2.2 E+4 1.4 E+' 5.7 E4 4.7 E4 1.3 E+5 5.5 E+5 1.2 E+5 5.2 E+8 ce - 144 1.5 E+5 7.0 E+7 3.9 E+5 1.0 E+10 8.6 E+5 1.3 E+10 8.2 E+5 1.1 E+10 I - 131 1.7 E+7 1.7 E+7 1.6 E+7 c.2 E+10 1.5 E+7 3.1 E+10 1.2 E+7 3.6 E+10 I - 133 3.6 E4 2.a E-6 3.8 E4 E.1 E.c 2.9 E.6 4.6 E ~ 2.2 E+6 5.3 E+E I - 135 7.0 E+5 2.5 E+i i.9 E.5 1.2 E+7 6.2 E+5 s.2 E-i 4.5 E+5 ~." E+i 4tidentified 4.1 E+7 0 1.0 E+8 1.4 E+12 1.1 E+8 8.3 E+11 9.9 E+7 6.7 E+11
%re'1/yr '92 - rren/yr 1
pCi e u0i/see 2-31 Rev. 8 7-1-82 i
Page 2 of 4 TAB 12 2-7 Ibse Pa mete Rg for NW Sector Pathey VeEetat,le Gardm Distarre 2'.2 miles X4 5.0 E-7 DC 1.9 E-9 Infant 0111d Tem Mult a11muclide Inhalatim Food & Grurd Inhalatim Focd & Grusd Lhalation Food & Grurd Inhalatim Focd & Grurd
'Pathey **Pathey Fathey Fathey Pathey Pathey Pathay Pathay H -
3 1.6 E+2 0 2.9 E+3 2.6 E+3 P -
3? 5.1 E+5 0 6.5 E+5 3.7 E+9 4.7 E+5 1.8 E+9 3 3 E+5 1.5 E+9 Cr - 51 1.2 E+6 7.3 E+6 7.5 E42 1.1 E+7 8 3 E42 1.7 E+7 M1 - 54 6.3 E+3 3.5 E+8 1.1 E+4 1.0 E+9 1.7 E 4 1.3 E+9 1.9 E 4 1.3 E+9 F; - 59 5.9 E+3 6.8 E+7 8.4 E+3 7.0 E.8 4.5 EA 1.0 E+9 4.7 E4 1.0 E+9 Co - 58 2.8 E+3 9.5 E+7 8.6 E+3 4.6 E+8 2.4 E4 6.8 E+8 2.7 E 4 7.0 E+8 Co - 60 8.0 E+3 5.4 E+9 2.4 E4 7.5 E+9 6.5 E4 8.6 E+9 7.1 E4 8.5 E+9 Zn - 65 1.6 EA 1.9 E+8 2.8 E 4 2.9 E+9 3.3 E4 2.1 E+9 2.6 E+4 1.5 E+9 Rb - 86 4.8 E4 2.3 E+6 5.0 E4 4.6 E 8 4.8 E4 1.8 E48 3.4 E4 2.2 E+8 Sr - 89 9.9 E+4 5.4 E+3 1.5 E+5 3.5 E+10 1.1 E6 1.5 E+10 7.6 E+4 9.8 E+9 Cr - 93 1.0 E+7 0 2.5 E+7 1.4 E+12 2.7 E+7 8.3 E+11 2.5 E+7 6.7 E+11 Y -
91 1.8 E+4 2.7 E+5 4.6 E+4 2.4 E+9 1.0 E+5 3.1 E+9 9.6 E+4 2.8 E+9 2r - 95 5.4 E+3 6. 3 E+7 1.5 E4 9.4 E+8 3.7 E+4 1.3 E+9 3.0 E4 1.3 E+9 Nb - 95 3.2 E+3 3.4 E+7 9.2 E+3 3 3 E+8 2.4 E+4 4.8 E+8 2.6 E 4 5.1 E4 Ru - 103 4.0 E+3 2.7 E+7 1.1 E+4 4.2 E8 2.7 E4 5.9 E+8 2.8 E4 5.8 E4 Ru - 106 4.1 E4 1.1 E+8 1.1 E+5 1.2 E+10 2.4 E+5 1.5 E+10 2.3 E+5 1.3 E+10 Ag - 110M 8.3 E+3 8.7 E+8 2.5 E4 4.0 E+9 6.8 E+4 5.2 E+9 7.6 E4 5.2 E 9 Cd - 1194 1.8 E4 0 4.6 E4 2.0 E+9 1.0 E+5 2.6 E+9 9.6 E+4 2.3 E+9 Sn - 123 7.4 E4 0 1.2 E+5 6.3 E+9 8.3 E+4 4.0 E4 7.8 E4 3.4 E+9 Cn - 126 2.9 E+5 f.5 E+9 5. ' E+5 3.0 E+ e.4 E+5 '.7 E+10 3.2 E+5 1.3 E+ v Sb 1.5 E, *.! E+t e.1 E- 2.3 E4 .C E+5 3.: E4 1.C E4 3.' E4 Sb - 125 3.7 E+3 5.S E+8 1.0 E 4 1.8 E+9 2.5 E 4 2.2 E+9 2.5 E+4 2.1 E4 T2 - 12714 9.4 E+3 2.3 E 3 1.6 E4 5.4 E+9 1.6 E+4 3.2 E4 1.1 E4 2.C E+9 T2 - 1294 7.9 E+3 4.9 E+6 1 3 E+4 2.9 E+9 1.3 E+4 1.8 E4 9.1 E43 1.2 E4 Cs - 134 1.8 E+5 1.7 F+9 2.5 E45 2.7 E+10 2.8 E+5 1.8 E+10 2.1 E+5 1.3 E+10 Cs - 136 3.4 E4 3.8 E+7 4.3 E4 2.6 E+8 4.8 I4 2.1 E+8 3 7 E4 2.1 E+B Cs - 137 1.5 E+5 2.6 E+9 2.1 E+5 2.7 E+10 2.1 E5 1.7 E+10 1.6 E+5 1.2 E+10 Ba - 140 1.4 E4 5.1 E+6 1.9 E 4 2.8 E+8 5.2 E4 2.2 E+8 5.5 E4 2.7 E+8 Ce - 141 5.4 E+3 3.4 E+6 1.4 E4 4.1 E+8 3.2 E4 5.4 E+8 3 0 E4 5.1 E+8 C2 - 144 3 7 EA 1.7 E+7 9.7 E-4 1.0 E+10 2.2 E+5 1.3 E+10 2.0 E+5 1.1 E+10 I - 131 37 E6 a.3 E-6 4.1 E-6 4.8 E+1: 3.7 E 6 3.1 E+10 3.0 E+6 3.8 E+'^
- 133 E.9 E+5 5.' I+E 9.5 E-5 8.1 E.! .3 E+5 c.6 E4 5.4 E+5 5.3 E4 I - 135 (.3 E+ 1.0 E+- *6 E+5
. C. - E- '.1 E+5 ~.2 Ee aidentifi d 1.0 E+7 0 2.5 E+7 1.4 E+12 2.7 E+7 e.3 E+4 2.5 E+7 4.7 E+11 Sre e r **r2 - rrm/yr pCL/h pC1/sec 2-32 pey, s 7-1-82
1 l
hee 3 of 4 l TAKI 2-7 1 Dose Parrete- R i for E Sector Pahy H:at (Cattle) Pathey Dista me 4.5 miles X4 1.2 E 7 D4 3.7 E-10 Infant (hild Teel Mult bjicrw.lide Inhalaticri Food & Gmurd Inhalatim Food & Gmmd Inhalatim Focd & Grourd Inhalatim Food & Gromd epa h y "Pahy Pathey Patha y Pa h y Pa h y Pathey Pathey H -
3 3.2 E+1 0 2.9 E+2 0 2.5 E+2 0 3.8 E42 0 P - 32 1.0 E+5 0 1.3 E+5 7.3 E+9 9.4 E4 3.4 E+9 6.6 E44 4.6 E+9 Cr - 51 1.8 E+1 2.3 E*5 5.4 E+1 6.5 E45 1.5 E*2 1.1 E+6 1.7 E 2 1.8 E+6 Hi - 54 1.3 E+3 6.9 E+7 2.1 E+3 7.6 E+7 3.3 E+3 8.1 E+7 3.9 E+3 9.2 E+7 F2 - 59 1.2 E+3 1.1 E+7 1.7 E+3 5.4 E+8 8.9 E+3 1.0 E+9 9.4 E+3 1.8 E+9 Co - 58 5.6 E+2 1.9 E+7 1.7 E+3 9.9 E+7 4.8 E+3 1.8 E+8 5.3 E+3 3 3 E+8 Co - 60 1.6 E+3 1.1 E*9 4.8 E+3 1.4 E+9 1 3 E4 1.7 E+9 1.4 E4 2.2 E+9 Zn - 65 3.1 E+3 3 7 E+7 5.7 E+3 9.4 E+8 6.7 E+3 8.2 E8 5.2 E+3 1.1 E+9 Rb - 86 9.5 E+3 4.5 E+5 9.9 E+3 5.4 E+8 9.5 E+3 3.8 E+8 6.8 E+3 4.6 E+8 Sr - 89 2.0 E+4 1.1 E+3 3.0 E+3 4.1 E+8 2.2 E+4 2.2 E+8 1.5 E 4 2.6 E+8 Sr - 90 2.0 E+6 0 5.1 E+6 8.6 E+4 5.4 E+6 6.7 E4 5.0 E+6 1.0 E+10 Y - 91 3.5 E+3 5.4 E4 9.2 E+3 2.0 E+8 2.0 E4 3.3 E 8 1.9 E4 5.2 E+8 Zr - 95 1.1 E+3 1 3 E+7 3.1 E+3 5.5 E+8 7.4 E+3 9.3 E+3 7.5 E+3 1.6 E+9 Nb - 95 6.3 E+2 6.8 E+6 1.8 E+3 2.0 E+9 4.8 E+3 3.7 E+9 5.2 E+3 6.8 E+9 Ra - 103 8.0 E42 5.4 E+6 2.2 E+3 3 5 E+9 5.4 E+3 6.2 E+9 5.5 E+3 1.1 E+10 Ru - 106 8.2 E+3 2.1 E+7 2.1 E4 5.6 E+10 4.8 E+4 9.1 E+10 4.6 E 4 1.5 E+11 Ag - 110! 1.7 E+3 1.7 E+8 5.0 E+3 8.1 E48 1.4 E+4 1.3 E4 1.5 E4 2.3 E+9 Cd - 119! 3.5 E+3 0 9.2 E+3 2.1 E+7 2.0 E~ 3.5 E+7 1.9 E4 5.3 E+7 Sn - 123 1.5 E+4 0 2.4 E4 7.1 E+9 1.7 E+; 5.7 E+ 1.6 E*4 4.1 E+9
.'ir. - 1N 5.3 E~ 9.3 E4 *2 E+5
. 2.3 E+K 8.7 E- 1. 3 E+" 6.3 E- 1.6 E40 2 - 12; 3." E+3 3. 0 E+7 5.2 E.3 1. 6 E+i 2.C E- 3.' E+5 2.C Eu 5.0 E-3
!b - 125 7.3 E+2 1.2 E+8 2.0 E+3 1.7 E+8 30 E+3 2.1 E+8 5.0 E+3 2.8 E+8 Ta - 12TM 1.9 E+3 4.6 E+3 3 2 E+3 5.0 E+9 5 3 E+3 3.7 E+9 2.3 E+3 4.4 E+9 T2 - 1294 1.6 E+3 9.8 E+5 2.5 E+3 4.9 E+9 2.6 E+3 3.7 E+9 1.8 E+3 4.5 E+9 Cs - 134 3.5 E+4 3.4 E.8 5.1 E4 1.5 E+9 5.6 E4 1.3 E+9 4.2 E44 1.6 E+9 Cs - 136 6.7 E+3 7.5 E46 8.5 E+3 5.0 E+7 9.7 E+3 4.3 E+7 7 3 E+3 5.3 E+7 Cs - 137 31 E4 5.1 E48 4.1 E+4 1.6 E+9 4.2 E44 1.3 E+9 31 E+4 1.5 E+9 Ib - 140 2.8 E+3 1.0 E+6 3.7 E+3 1.3 E+7 1.1 E4 3.6 E+7 1.1 E4 3.8 E+7 Ce - 141 1.1 E+3 6.8 E45 2.8 E+3 1.3 E+7 6.3 E+3 2.1 E+7 6.0 E+3 3 3 E+7 Ce - 144 7.4 E+3 3.5 E+6 1.9 E+4 1.5 E+8 4.3 E+4 2.5 E-8 4.1 E4 3.9 E+8 I - 131 7.4 E+5 S.6 E4 S.1 E+5 5.4 E4 7.3 E+5 3.6 E+9 6.0 E*5 5.0 E4 I - 133 1.5 E+5 '2. Ed
- 9 I+5
. 1.2 F- 1.5 E-i '.2 E+5 1.1 E~ 1.2 E-f I - 135 3.5 E+4 1 3 E.5 4.0 E+4 1.3 E+5 3.1 E~
- 3 E+5
. 2.2 E~ 1.3 E4 niidattified 2.0 E+6 0 5.1 E+6 8.6 E+9 5.6 E+6 6.7 E+9 5.0 E+6 1.0 E+13
- TeVyr "5 - mn'yr pCUM pC1/sec 2-33 8 gev.82 7
P T
s Page 4 of 4 TABLE 2-7 Dose Para,ete R i for }lM Sector P;ttMay Milk Pahy Distarre 4.5 miles X4 1.2 E-7 D4 3.7 E-10 Infant Child Teen Adult l
lRadionuclide Inhalatim Food & Grotid Inhalaticn Focd & Gromd Inhalatim Food & Cmid Inhalatim Food & Gromd l 'Pahy "Pathey Pathway Pathay Pa h y Pa h y Pathey Pa h y H - 3 2.4 E+3 0 1.6 E+3 0 9.9 E42 0 7.6 E+20 P - 32 0 1.6 E+11 0 7.6 E+10 0 3.1 E+to 0 1.7 E+10 Cr - 51 0 4.2 E+6 0 4.8 E+6 0 7.5 E+6 0 6.4 E+6 Hi - 54 0 3.1 E+7 0 1.7 E+7 0 2.3 E+7 0 2.1 E+7 Fa - 59 0 3.4 E+8 0 1.7 E+8 0 2.5 E*S 0 2.0 E+8 Co - 58 0 5.0 E+7 0 5.9 E+7 0 9.1 E+7 0 7.9 E+7 Co - 60 0 1.7 E+8 0 1.9 E48 0- 2.9 E4 0 2.4 E+8 2n - 65 0 1.7 E+10 0 9.9 E+9 0 6.6 E+9 0 3.9 E+9 fb - 86 0 2.1 E+10 0 8.2 E+9 0 4.4 E+9 0 2.4 E+9 Sr - 89 0 1.1 E+10 0 5.6 E+9 0 2.3 E+9 0 1.2 E+9 Sr - 90 0 1.0 E+11 0 9.3 E+10 0 5.5 E+10 0 3.9 E+10 Y - 91 0 4.4 E+6 0 4.4 E+6 0 5.4 E+6 0 4.0 E+6 Er - 95 0 6.9 E+5 0 7.4 E5 0 1.0 E+6 0 8.0 E+5 Nb - 95 0 1.8 E+8 0 2.0 E+8 0 2.9 E+8 0 2.4 E+8 Ru - 103 0 9.2 E4 0 9.6 E+4 0 1.3 E+5 0 1.0 E+5 RJ - 106 0 1.2 E+6 0 1.2 E+6 0 1.4 E+6 0 1.1 E+6 Ag - 110M 0 1.2 E+10 0 1.6 E+10 0 2.1 E+10 0 1.8 E+10 Cd - 119: 0 5.7 E+7 0 5.1 E+7 0 6.4 E+7 0 4.6 I+7 Sr. - 123 0 3. ~ E4 0 2.0 E4 0 1.2 E+9 0 6.E E4
- 2. 26
- i. i E+s 0 5.4 E. 2.3 E+9 0 1.3 E4 Sb - 124 0 5.4 E+8 0 5.7 E+8 0 ~.S E+6 0 6.1 E+6 Ib - 125 0 1.6 E4 0 1.6 E-6 0 2.2 E+8 0 1.8 E+6 TJ - 127M 0 1.0 E+9 0 5. 8 E+8 0 3 3 E+8 0 1.8 E+8 T2 - 1294 0 1.3 E+9 0 7.5 E+8 0 4.3 E4 0 2.4 E4 Cs - 134 0 5.4 E+10 0 2.9 E+1C 0 .B E+10 0 1.1 E+10 Cs - 136 0 5.5 E+9 0 2.6 E+9 0 1.7 E+9 0 9.9 E+8 Cs - 137 0 4.9 E+10 0 2.5 E+10 0 1.4 E+10 0 8.1 E+9 Da - 140 0 2.3 E4 0 1.1 I+8 0 7.2 E+7 0 5.3 E+7 Ce - 141 0 1.2 E+7 0 1.2 E+7 0 1.5 E+7 0 1.1 E+7 Ce - 144 3 1.1 E4 0 1.0 E.E 0
- 3 E+3
. 0 9.6 E+7
.- E. : ; .: 3 E.-
^
2.: f. i a ".; E.1-I - 133 0 9.5 E+) 0 3.9 E+9
^
".' E9 0 9.9 E4 I - 135 0 2.0 E+7 0 8.5 E+6 0 3.7 E4 0 2.2 E46
%1dentified 0 1.0 E+11 0 9 3 E+10 0 5.5 E+10 0 3.9 E+10
've .' y- **r2 - crer.'yr p C1/F LCi/sec 2-3" Rev. 8 7-1-82
Page 1 of 1 TABE 2-8 Dose Paranete R 1 for N Sector Pathay Milk Pathay Distance 4.5 miles X4 7.0 E-6 D4 3 5 E-10 Infant 0111d Teen Adult ladionuclide Inhalatim Food & Gmad Inhalation Food & Gromd Inhalation Food & Gmad Inhalatim Food & Gmsd ePathey "Pathey Pathey Pathay Fathey Pathay Pathay Pathey H- 3 0 2.4 E+3 0 1.6 E+3 0 9.9 E+2 0 7.6 E420 P - 32 0 1.6 E+11 0 7.6 E+10 0 3.1 E+10 0 1.7 E+10 Cr - 51 0 4.2 E+6 0 4.8 E+6 0 7.5 E+6 0 6.4 E+6 M1 - 54 0 3.1 E+7 0 1.7 E+7 0 2.3 E+7 0 2.1 E+7 F2 - 59 0 3.4 E+8 0 1.7 E+8 0 2.5 E+8 0 2.0 E+8 Co - 58 0 5.0 E+7 0 5.9 E+7 0 9.1 E+7 0 7.9 E+7 Co - 60 0 1.7 E+8 0 1.9 E+8 0 2.9 E+8 0 2.4 E+8 2n - 65 0 1.7 E+10 0 9.9 E+9 0 6.6 E+9 0 3.9 E+9 Rb - 86 0 2.1 E+10 0 8.2 E+9 0 4.4 E+9 0 2.4 E+9 Sr - 89 0 1.1 E+10 0 5.6 E+9 0 2.3 E+9 0 1.2 E+9 Sr - 90 0 1.0 E+11 0 9.3 E+10 0 5.5 E+10 0 3.9 E+10 Y - 91 0 4.4 E+6 0 4.4 E+6 0 5.4 E+6 0 4.0 E+6 Zr - 95 0 6.9 E45 0 7.4 E+5 0 1.0 E+6 0 8.0 E45 Nb - 95 0 1.6 E+8 0 2.0 E+8 0 2.9 E+8 0 2.4 E+8 Ru - 103 0 9.2 E+4 0 9.6 E+4 0 1.3 E+5 0 1.0 E+5 R2 - 106 0 1.2 E+6 0 1.2 E46 0 1.4 E+6 0 1.1 E+6 Ag - 110M 0 1.2 E+10 0 1.6 E+10 0 2.1 E+10 0 1.8 E+10 Cd - 11cM 0 5.7 E+7 0 5.1 E+7 0 6.4 E+7 0 4.6 E+7 I:h - 123 0 37 E+9 0 2.0 E+9 1.2 E+9 0 8.5 E 6
, Sr. - 126 3 5.9 I+9 0 5.4 I+9 : 2.3 E+; O 1. :- E+9 Sb - 124 0 5.4 E8 0 5.7 E+8 0 7.8 E48 0 6.1 E48 Sb - 125 0 1.6 E+8 0 1.6 E46 0 2.2 E*8 0 1.B E+8
, T2 - 12m 0 1.0 E+9 0 5.8 E48 0 3 3 E+8 0 1.E E+$
1 T2 - 129M 0 1.3 E+9 0 7.5 E+8 0 4.3 E+8 0 2.4 E+8 Cs - 134 0 5.4 E+10 0 2.9 E+10 0 1.8 E+10 0 1.1 E+10 Cs - 136 0 5.5 E+9 0 2.6 E+9 0 1.7 E+9 0 9.9 E+S Cs - 137 0 4.9 E+10 0 2.5 E+10 0 1.4 E+10 0 8.1 E49
% - 140 0 2.3 E+8 0 1.1 E+8 0 7.2 E+7 0 5.3 E+7 Ce - 141 0 1.2 E+7 0 1.2 E+7 0 1.5 E+7 0 1.1 E+7 Ce - 144 0 1.1 E+8 0 1.0 E+8 0 1.3 E+8 0 9.6 E+7 I - 131 3 *: E+12
. 0 4.3 E+11 C 2.2 E+11 0 1.' E+' "
I - 133 0 9.6 E+9 0 3.9 I+9 1.- E+9
~
9.9 I-:
1 I - 135 0 2.0 E+7 0 8.5 E46 0 3 7 E+6 0 2.2 E.6 0 1.0 E+11 0 9.3 E+10 0 5.5 E+10 0 3.9 E+10 hidentified l
'mWyr **r2 - creVyr pC1/h pCi/sec l
2-35 p,y, g 7 82
Page 1 of 1 TABE 2-9 Ibse Paraneta- R1 for M Sector Pathey Milk Pathwy Distarce 4.5 miles X4 6.0 E-8 DS 3.2 E-10 Infant Child Teen Mult
- alimuclide Inhalation Food & Grund
. Inhalaticri Food & Grurd Inhalatim Food & Grurd Inhalatim Food & Grund
'Pathey **Pathey Pathey Pathey Pathey Pathey Pathey Pathey H- 3 0 2.4 E+3 0 1.6 E+3 0 9.9 E+2 0 7.6 E+20 P - 32 0 1.6 E+11 0 7.6 E+10 0 3.1 E+10 0 1.7 E+10 Cr - 51 0 4.2 E+6 0 4.8 E+6 0 7.5 E+6 0 6.4 E+6 M1 - 54 0 3.1 E+7 0 1.7 E+7 0 2 3 E+7 0 2.1 E+7 F2 - 59 0 3.4 E+8 0 1.7 E+8 0 2.5 E+8 0 2.0 E+8 03 - 58 0 5.0 E+7 0 5.9 E+7 0 9.1 E+7 0 7.9 E+7 Co - 60 0 1.7 E+8 0 1.9 E+8 0 2.9 E+8 0 2.4 E+8 2n - 65 0 1.7 E+10 0 9.9 E+9 0 6.6 E+9 0 3.9 E+9 Pb - 86 0 2.1 E+10 0 8.2 E+9 0 4.4 E+9 0 2.4 E+9 Sr - 89 0 1.1 E+10 0 5.6 E+9 0 2.3 E+9 0 1.2 E+9 Sr - 90 0 1.0 E+11 0 9.3 E+10 0 5.5 E+10 0 3.9 E+10 Y- 91 0 4.4 E.6 0 4.4 E+6 0 5.4 E+6 0 4.0 E+6 Zr - 95 0 6.9 E+5 0 7.4 E45 0 1.0 E+6 0 8.0 E45 Nb - 95 0 1.8 E+8 0 2.0 E+8 0 2.4 E+8 0 2.4 E+8 Ru - 103 0 9.2 E+4 0 9.6 E+4 0 1.3 E+5 0 1.0 E+5 PJ - 106 0 1.2 E+6 0 1.2 E+6 0 1.4 E+6 0 1.1 E+6 Ag - 1101 0 1.2 E+10 0 1.6 E+10 0 2.1 E+10 0 1.5 E.10 Cd - 1191 0 5.7 E.' O 5.1 E+7 0 6.4 E+7 0 4.f E+7 31 - 123 0 3.' E4 0 2.0 E4 C 1.2 E+9 0 6.: E4 Sr. '26 C 5.9 E4 0 5.- E+9
^
2.3 E4 0 "3 E+i Sb - 124 0 5.4 E8 0 5.7 E+8 C 7.8 E+8 0 6.' E4 Sb - 125 0 1.6 E.8 0 1.6 E+8 0 2.2 E+8 0 1.5 E+8 l T2 - 127M 0 1.0 E 9 0 5.8 E+8 0 3 3 E+8 0 1.6 E4 Te - 1?94 0 1.3 E+9 0 7.5 E+8 0 4.3 E+8 0 2.4 E+8 0 5.4 E+10 0 2.9 E+10 0 1.8 E+10 0 1.1 E+1 C Cs - 134
! Cs - 136 0 5.5 E+9 0 2.6 E+9 0 1.7 E+9 0 9.9 E+8 l C3 - 137 0 4.9 E+10 0 2.5 E+10 0 1.4 E+10 0 8.1 E+9 La - 140 0 2.3 E+8 0 1.1 E+8 0 7.2 E+7 0 5.3 E+7 0 1.2 E+7 0 1.2 E+7 0 1.5 E+7 0 1.* E+7 l Ce - 141 2-10 0 1.1 E4 0 1.0 E4 0 1.3 E+8 0 9.5 E+7 2.2 E+'1 ~.- E+"
l: - *3* C .: E *2 0 L.3 E.11 0 9.: E4
- I 133 C 9.5 E4 0 3.9 E+';
- 1.7 E+9 0 0 2.0 E+7 0 8.5 E+6 0 3 7 E+6 0 2.2 E46 l I - 135 0 3.9 E+10 pidmtified 0 1.0 E+11 0 9.3 E+10 0 5.5 E+10
- xedye ** 2 - mredy-pC1/M pCi/sec 2-36 g,y, g 7-1-52
Page 1 of 1 TAKE 2-10 Ibse Para,eter Ri for g Sector Pathey Milk Pathay Dis + m 4.5 miles X4 4.5 E-8 DM 2.9 E-10 Infant Orild Teen Adult Ra11cnuclide Inhalatim Food & Gmmd Inhalatim Food & Ground Inhalatim Food & Gnxsd Inhalatim Food & Gromd
'Pathay **Pathey Fathay Fathey Fathay Pathay Pathey Pathey H- 3 0 2.4 E+3 0 1.6 E+3 0 9.9 E+2 0 7.6 E*20 P -
32 0 1.6 E+11 0 7.6 E+10 0 3.1 E+10 0 1.7 E+10 cr - 51 0 4.2 E+6 0 4.8 E46 0 7.5 E+6 0 6.4 E46 m - 54 0 3.1 E+7 0 1.7 E+7 0 2.3 E+7 0 2.1 E+7 Fa - 59 0 3.4 E+8 0 1.7 E+8 0 2.5 E48 0 2.0 E+8 Co - 58 0 5.0 E+7 0 5.9 E47 0 9.1 E+7 0 7.9 E+7 Co - 60 0 1.7 E.8 0 1.9 E48 0 2.9 E 8 0 2.4 E+8 Zn - 65 0 1.7 E+10 0 9.9 E+9 0 6.6 E+9 0 3.9 E+9 lb - 86 0 2.1 E+10 0 8.2 E+9 0 4.4 E+9 0 2.4 E+9 Sr - 89 0 1.1 E+10 0 5.6 E+9 0 2.3 E+9 0 1.2 E+9 Sr - 90 0 1.0 E+11 0 9.3 E+10 0 5.5 E+10 0 3.9 E+10 Y- 91 0 4.4 E+6 0 4.4 E+6 0 5.4 E+6 0 4.0 E+6 Zr - 95 0 6.9 E+5 0 1.4 E+5 0 1.0 E+6 0 8.0 E45 Nb - 95 0 1.8 E+8 0 2.0 E+8 0 2.4 E+8 0 2.4 E+8 Ru - 103 0 9.2 E+4 0 9.6 E+4 0 1.3 E+5 0 1.0 E+5 RJ - 106 0 1.2 E+6 0 1.2 E+6 0 1.4 E+6 0 1.1 E+6 Ag - 11 m 0 1.2 E+10 0 1.6 E+10 0 2.1 E+10 0 1.8 E+10 Cd - 1191 0 5.7 E+' O 5.1 E+7 0 6.4 E.7 0 4.6 E+7 Sn - 123 0 3.7 E+9 0 2.0 E4 0 1.2 E+9 0 S.6 E4 Sn - 126 0 8.9 E+9 0 5 ; I+9 2.3 E+9 C i.3 E+9 Sb - 124 0 5.4 E+8 0 5.7 E+8 0 7.8 E+3 0 6.1 E+8 Sb - 125 0 1.6 E.8 0 1.6 E+8 0 2.2 E+8 0 1.8 E+8 Ta - 12i11 0 1.0 E+9 0 5.8 E.8 0 3 3 E+8 0 1.8 E+8 Te - 1294 0 1 3 E+9 0 7.5 E+8 0 4.3 E+8 0 2.4 E+8 Cs - 134 0 5.4 E+10 0 2.9 E+10 0 1.8 E+10 0 1.1 E+10 Cs - 136 0 5.5 E+9 0 2.6 E+9 0 1.7 E+9 0 9.9 E+8 Cs - 137 0 4.9 E+10 0 2.5 E+10 0 1.4 E+10 0 8.1 E+9 Ba - 140 0 2.3 E+8 0 1.1 E+8 0 7.2 E+7 0 5.3 E+7 Ce - 141 0 1.2 E+7 0 1.2 E+7 0 1.5 E+7 0 1.1 E+7 Ce - 144 0 1.1 E+8 0 1.0 E+8 0 1.3 E+8 0 9.6 E+7 I '31 0 1. 0 E+' 2 0 .3 E+'1 : 2.2 E+~1 0 1.L E+~~
I - 133 0 9.5 E+i L 3.9 E+9 C 1.7 E+) 0 9.9 E+i I - 135 0 2.0 E+7 0 8.5 E+6 0 3.7 E+6 0 2.2 E+6 Unidentified 0 1.0 E+11 0 9.3 E+10 0 5.5 E+10 0 3.9 E+13
- mrevye *d - mrev'y-pCi/M pCi/see 2-37 g,y, g 7-1-82
l i
i Page 1 of 1 !
TABE 2-11 Ibse Paranete- Ri for g Secur l
l Pattney Milk Pathay Distance 4.5 miles X4 4.8 E-8 D4 3.4 E-10 Infant 0111d ' Deen Adult ionuclide Inhalation Food & Gromd Inhalatim Food & Gmad Inhalation Food & Gmrd Inhalation Food & Gn:md
'Pathay Mathay hthey Pathey Pathway Pathey Pathey Pathay H -
3 0 2.4 E+3 0 1.6 E+3 0 9.9 E42 0 7.6 E+20 P -
32 0 1.6 E+11 0 7.6 E+10 0 3.1 E+10 0 1.7 E+10 Cr - 51 0 4.2 E+6 0 4.8 E46 0 7.5 E+6 0 6.4 E46 m - 54 0 31 E+7 0 1.7 E+7 0 2.3 E+7 0 2.1 E+7 Fa - 59 0 3.4 E+8 0 1.7 E+8 0 2.5 E 8 0 2.0 E+8 Co - 58 0 5.0 E+7 0 5.9 E+7 0 9.1 E+7 0 7.9 E+7 Co - 60 0 1.7 E48 0 1.9 E48 0 2.9 E48 0 2.4 E+8 2n - 65 0 1.7 E+10 0 9.9 E+9 0 6.6 E+9 0 3.9 E+9 lb - 86 0 2.1 E+10 0 8.2 E+9 0 4.4 E9 0 2.4 E+9 Sr - 89 0 1.1 E+10 0 5.6 E+9 0 2.3 E+9 0 1.2 E+9 Sr - 90 0 1.0 E+11 0 9.3 E+10 0 5.5 E+10 0 3 9 E+10 Y - 91 0 4.0 E+6 0 4.4 E+6 0 5.4 E+6 0 4.0 E+6 Zr - 95 0 6.9 E+5 0 7.4 E+5 0 1.0 E46 0 8.0 E+5 Nb - 95 0 1.8 E.8 0 2.0 E+8 0 2.9 E+8 0 2.4 E+8 Ru - 103 0 9.2 E44 0 9.6 E+4 0 1.3 E+5 0 1.0 E+5 Ru - 106 0 1.2 E+6 0 1.2 E+6 0 1.4 E+6 0 1.1 E+6 Ag - 11CN 0 1.2 E+10 0 1.6 E+10 0 2.1 E+10 0 1.8 E+10 Cd - 11 P 0 5.7 E+7 0 5.1 E+7 0 6.4 E+7 0 4.6 E+7 Sn - 123 0 3.7 E4 0 2.0 E4 0 1.2 E-9 3 8.8 E4 Sr. - 126 0 6.9 E+i D 5.0 E4 0 2.3 E-9 -
1.3 E4 Sb - 124 0 5.4 E+8 0 5.7 E+8 0 7.8 E 8 0 6.1 E+8 Sb - 125 0 1.6 E+8 0 1.6 E+8 0 2.2 E+8 0 1.8 E+8 T2 - 127M 0 1.0 E+9 0 5.8 E48 0 3 3 E+8 0 1.8 E+8 Te - 129M 0 1.3 E+9 0 7.5 E+8 0 4.3 E+8 0 2.4 E+8 Cs - 134 0 5.4 E+10 0 2.9 E+10 0 1.8 E+10 0 1.1 E+10 Cs - 136 0 5.5 E6 0 2.6 E+9 0 1.7 E+9 0 9.9 E+8 cs - 137 0 4.9 E+10 0 2.5 E+10 0 1.4 E+10 0 8.1 E+9 Ba - 140 0 2 3 E+8 0 1.1 E+8 0 7.2 E+7 0 5.3 E+7 ce - 141 0 1.2 E+7 0 1.2 E+7 0 1.5 E+7 0 1.1 E+7 Ce - 144 0 1.1 E8 0 1.0 E+8 0 1.3 E+8 0 9.6 E+7 I - 131 0 1.3 E+'2 C 4.3 E+11 0 2.2 E+11 3 1.4 E+11 I - 133 0 9.6 E+i 0 3.9 I-9 0 1.7 E4 : 3.9 E 4 I - 135 0 2.0 E+7 0 8.5 E46 0 3 7 E46 0 2.2 E46 Didentified 0 1.0 E+11 0 9.3 E+10 0 5.5 E+10 0 3.9 E+10 N:revyr '52 - treVyr uCi/M aCi/see 2-3B g,y, g 7-1-s2
l l
l Page 1 of 1 TABE 2-12 !
Ibse Paranets R1 for E_ Sector Pathay Milk Pathay Distance 4.5 miles X4 5.8 E-8 DM 4.7 E-10 Infant Child Teert Adult
- adionuclide Inhalatim Food & Gromd Inhalation Food & Gromd Inhalatim Food & Gromd Inhalatim Food & Grumd
'Pathay **Pathay Pathay Pathe y Pathay Pathay Pathey Pathay H - 3 0 2.4 E+3 0 1.6 E+3 0 9.9 E42 0 7.6 E420 P -
32 0 1.6 E+11 0 7.6 E+10 0 3.1 E+10 -0 1.7 E+10
.Cr - 51 0 4.2 E+6 0 4.8 E*6 0 7.5 E46 0 6.4 E46 ft) - 54 0 31 E+7 0 1.7 E+7 0 2.3 E+7 0 2.1 E+7 F2 - 59 0 3.4 E*8 0 1.7 E+8 0 2.5 E+8 0 2.0 E+8 Go - 58 0 5.0 E+7 0 5.9 E+7 0 9.1 E+7 0 7.9 E+7
' Co - 60 0 1.7 E+8 0 1.9 E+8 0 2.9 E48 0 2.4 E48 Zn - 65 0 1.7 E+10 0 9.9 E+9 0 6.6 E+9 0 3 9 E+9 Ib - 86 0 2.1 E+10 0 8.2 E+9 0 4.4 E+9 0 2.4 E+9 3- 89 0 1.1 E+10 0 5.6 E+9 0 2.3 E+9 0 1.2 E+9 Sr - 90 0 1.0 E+11 0 9.3 E+10 0 5.5 E+10 0 3 9 E+10 Y- 91 0 4.4 E+6 0 4.4 E+6 0 5.4 E+6 0 4.0 E+6
' Zr - 95 0 6.9 E+5 0 7.4 E+5 0 1.0 E+6 0 8.0 E45 Nb - 95 0 1.8 E+8 0 2.0 E+8 0 2.9 E+8 0 2.4 E+8
- Ib - 103 0 9.2 E+a 0 9.6 E+.4 0 1.3 E+5 0 1.0 E+5 lb - 106 0 1.2 E+6 0 1.2 E+6 0 1.4 E+6 0 1.1 E46 Ag - 110M 0 1.2 E+10 0 1.6 E+10 0 2.1 E+10 0 1.8 E+10 Cd - 1131 0 5.7 E+7 0 5.1 E+7 0 6.4 E+7 0 4.6 E+7 31 - 123 0 3.7 E4 0 2.0 E+9 0 1.2 E.9 0 8.8 E+8 Sn - 126 0 E.9 E4 C 5.4 E-9 0 2.3 E 9 0 1.3 E+9
'35 - 124 0 5.- Ed : 5.7 E4 0 7.6 E4 0 6.1 E4 Sb - 125 0 1.6 E+E O 1.6 E+8 0 2.2 E8 0 1.8 E+8 Te - 127M 0 1. 3 E4 0 5.8 E+8 0 3.3 E+8 0 1.8 E+$
T2 - 1291 0 1.3 E+9 0 7.5 E+8 0 4.3 E+8 0 2.4 E.8 0 5.4 E+10 0 2.9 E+10 0 1.8 E+10 0 1.1 E+10
'Cs - 134 Cs - 136 0 5.5 E+9 0 2.6 E+9 0 1.7 E+9 0 9.9 E+8 Cs - 137 0 4.9 E+10 0 2.5 E+10 0 1.4 E+10 0 8.1 E+9 E3 - luo 0 2.3 E.8 0 1.1 E+8 0 7.2 E+7 0 5.3 E+7 Ce - 141 0 1.2 E+' C 1.2 E+7 0 1.5 E+7 0 1.1 E+7 Ce - 144 0 1.1 E+8 0 1.0 E+8 0 1.3 E+8 0 9.6 E+7 1.0 E.*2 a.3 E+11 0 2.2 E+11 0 1.4 E+11 I - 131 0 0 9.9 E4
- - 133 0 9.i I-i 0 3.9 E-9 0 1.7 I+9 0 2.2 E~ : 6.5 E4 0 3.7 E-6 0 2.2 E+f I - 135 0 hidentified 0 1.0 E+1' 0 9.3 E+10 0 5.5 E+10 0 3.9 E+10 N:revyr '52 - creVyr pCi/M .:Ci/sec 2-39 Sev. 8 7-1-82
Page 1 of 2 TABI 2-13 Ibse Pa aneta-1R for g Sector Pattney Ca p Store Distance 0.60 miles X4 3.1 E-6 DM 2.8 E4 Infant 0111d Teen Adult Wimuclide Inhalatim Food & Grurd Inhalation Food & Grund Inhalatim Food & Grourd Inhalatim Food & Grurd
'Pathay HPathay Fathay Fathey Pathay Pathey Pathay Pathay 2.6 E+2 0 2.9 E42 0 2.9 E+2 0 H- 3 1.5 E+2 0 5.9 E+5 0 4.3 E+5 0 3 0 E+5 0 P- 32 4.6 E+5 0 1.1 E+6 2.5 E+2 1.1 E46 6.8 E42 1.1 E+6 7.6 E42 1.1 E+6 Cr - 51 8.2 E+1 m - 54 5.8 E+3 3.2 E 8 9.8 E+3 3.2 E+8 1.5 E 4 3.2 E+8 1.8 E+4 3.2 E+8 F2 - 59 5.4 E+3 6.2 E+7 7.6 E+3 6.2 E+7 4.1 E4 6.2 E+7 4.3 E4 6.2 E+7 Co - 58 2.5 E+3 8.7 E+7 7.8 E+3 8.7 E+7 2.2 E 4 8.7 E+7 2.4 E4 8.7 E+7 Co - 60 7.3 E+3 4.9 E+9 2.2 E4 4.9 E+9 5.9 E4 4.9 E+9 6.5 E4 4.9 E+9 Zn - 65 1.4 E4 1.7 E+8 2.6 E+4 1.7 E+8 3.1 E+4 1.7 E+8 2.4 E4 1.7 E+8 m - 86 4.3 E4 2.1 E+6 4.5 E4 2.1 E+6 4.3 E4 2.1 E+6 31 E4 3.1 E+6 Sr - 89 9.1 E4 4.9 E+3 1.4 E+5 4.9 E+3 9.9 E 4 4.9 E+3 6.9 E+4 4.9 E+3 0 2.5 E+7 0 2.3 E+7 0 Sr - 90 9.3 E+6 0 2.3 E+7 Y- 91 1.6 E 4 2.3 E+5 4.2 E+4 2.5 E+5 9.3 E+4 2.5 E+5 8.8 E 4 2.5 E+5 Zr - 95 5.0 E+3 5.7 E+7 1.4 E4 5.7 E+7 34 E+4 5.7 E+7 3.4 E4 5.7 E+7 Nb - 95 2.9 E+3 31 E+7 8.4 E+3 3.1 E+7 2.2 E4 3.1 E+7 2.4 E4 3.1 E+7 Ru - 103 3.7 E+3 2.5 E+7 1.0 E44 2.5 E+7 2.5 E4 2.5 E+7 2.5 E4 2.5 E+7 lu - 106 3.7 E 4 9.7 E+7 9.8 E 4 9.7 E+7 2.2 E45 9.7 E+7 2.1 E+5 9.7 E+7 Ag - 11(N 7.5 E+3 7.9 E+6 2.3 E44 7.9 E46 6.2 E4 7.9 E+3 6.9 E4 7.9 E+8 Cd - 1191 1.6 E 4 0 4.2 E4 0 9.3 E4 0 6.0 E+4 0 Sh - 123 6.7 E4 0 1.1 E+5 0 7.6 E 4 0 7.2 E4 0 Cr. - 126 2.7 E+5 f.' :+; : 3 E4
. 6.3 E-9 4.0 E+5 6.0 E9 2.9 E+5 6.0 E+9 3 7 E4 1.4 E+8 9.1 E4 1.4 E+3 9.3 E44 1.4 E+6 S0 - 124 1.3 E4 1.4 E+6 Sb - 125 3.4 E+3 5.3 E4 4.2 E+3 5.3 E+8 2.3 E+4 5.3 E+8 2.3 E4 5.3 E 4 Te - 127M 8.6 E+3 2.1 E+4 1.5 E4 2.1 E4 1.5 E4 2.1 E4 1.0 E4 2.1 E+4 T3 - 1291 7.3 E+3 4.5 E+6 1.1 E+4 4.5 E+6 1.2 E 4 4.5 E46 8.3 E+3 4.5 E+6 1.6 E+5 1.6 E+9 2.3 E.5 1.6 E+9 2.6 E45 1.6 E+9 1.9 E+5 1.6 E+9 Cs - 134 Cs - 136 3.1 E+4 3.4 E+7 3.4 E+4 3.4 E+7 4.4 E4 3.4 E+7 3.3 E 4 34 E+7 Cs - 137 1.4 E45 2.3 E+9 1.9 E45 2.3 E+9 1.9 E+5 2.3 E.9 1.4 E+5 2.3 E+9 Ib - 140 1.3 E+4 4.7 E+6 1.7 E4 4.7 E+6 5.2 E4 4.7 E+6 5.0 E+4 4.7 E4 Ce - 141 4.9 E+3 31 E+6 1.3 E44 3.1 E+6 2.9 E4 31 E+6 2.7 E44 3.1 E46 Ce - 144 1.6 E+7 8.9 E4 1.0 E+7 2.0 E+5 1.6 E+7 1.9 E+5 1.6 E+7 3.4 E+4 I - 131 3.4 E4 39E4 3.7 E4 3 9 E+6 3.3 E+6 3.9 E4 2.7 E4 3.9 E+i 1 - 133 8.1 E+5 5.i E4 E.5 E-5 5.6 E+5 6.7 E+5 5.6 E4 4.9 E+5 5.f E*?
I - 135 1.6 E+5 5.8 E+5 1.8 E45 5.8 E+5 1.4 E+5 5.6 E+5 1.0 E+5 5.8 E4 2.7 E+7 0 2.3 E+7 0 Jnidetified 9.3 E46 0 2.3 E+7 0
'nrevy- **:2 - crevyr pCi/M uCi/see 2 40 p,y, g i 7-1-82
I Page 2 of 2 TABIE 2-13 Dase Paraneter R 1 for ESE Sector Pathay Milk Pathey Distance 4.5 miles X4 7.0 E-8 D4 5.8 E-10 Infant 0111d Teen Adult adionuclide Inhalation Food & Grund Inhalation Food & Gromd Inhalation Food & Ground Inhalation Food & Orund
'Pathay **Pathay Pathay Pathay Pathay Pathay Pathey Pathway H -
3 0 2.4 E+3 0 1.6 E+3 0 9.9 E42 0 7.6 E420
'P -
32 0 1.6 E+11 0 7.6 E+10 0 31 E+10 0 1.7 E+10 Cr - 51 0 4.2 E46 0 4.8 E46 0 7.5 E46 0 6.4 E46
. * - 54 0 31 E+7 0 1.7 E+7 0 2.3 E+7 0 2.1 E+7 F2 - 59 0 34 E+8 0 1.7 E+8 0 2.5 E+8 0 2.0 E48
- Go - 58 0 5.0 E+7 0 5.9 E+7 0 9.1 E+7 0 7.9 E+7 Go - 60 0 1.7 E48 0 1.9 E+8 0 2.9 E48 0 2.4 E48 Zn - 65 0 1.7 E+10 0 9.9 E+9 0 6.6 E+9 0 3 9 E+9 6 - 86 0 2.1 E+10 0 8.2 E49 0 4.4 E49 0 2.4 E49
'Sr - 89 0 1.1 E+10 0 5.6 E+9 0 2.3 E+9 0 1.2 E+9 Sr - 90 0 1.0 E+11 0 9.3 E+10 0 5.5 E+10 0 3 9 E+10 Y - 91 0 4.4 I+6 0 4.4 E+6 0 5.4 E+6 0 4.0 E+6 Zr - 95 0 6.9 E+5 0 7.4 E+5 0 1.0 E+5 0 8.0 E+5 2- 95 0 1.8 E+8 0 2.0 E+8 0 2.9 E+8 0 2.4 E+8 Ru - 103 0 9.2 E4 0 9.6 E+4 0 1.3 E+5 0 1.0 E45 lb - 106 0 1.2 E.6 0 1.2 E+6 0 1.4 E+6 0 1.1 E46
- Ag - 1101 0 1.2 E+10 0 1.6 E+10 0 2.1 E+10 0 1.3 E+10
- Cd - 115M 0 5.7 E.? O 5.1 E+7 0 6.c E+7 0 4.6 E+7
. 9) - 123 0 3.7 E4 0 2.0 E+9 0 1.2 E+9 0 6.5 Ee Sn - 126 0 3.9 E-i 0 5.:. E-9 0 2.3 E+9 C
- 3 E-9 Sb - 12u 0 5.4 E-5 0 5.7 E.8 0 7.8 E+8 0 6.1 E+S Sb - 125 0 1.6 E.8 0 1.6 E+8 0 2.2 E+8 0 1.6 E+8 Ta - 127M 0 1.0 E+9 0 5.8 E+8 0 3.3 E+8 0 1.6 E+S Te - 1291 0- 1.3 E+9 0 7.5 E 8 0 4.3 E+8 0 2.4 E+8 0 5.4 E+10 0 2.9 E+10 0 1.8 E+10 0 1.1 E+10 lCs-134 2.6 E+9 0 1.7 E+9 0 9.9 E+8 Cs - 136 0 5.5 E+9 0
- Cs - 137 0 4.9 E+10 0 2.5 E+10 0 1.4 E+10 0 8.1 E+9
,Ib - 1u0 0 2.3 E 8 0 1.1 E+8 0 7.2 E+7 0 5.3 E+7 Ce - 141 0 1.2 E+7 0 1.2 E+7 0 1.5 E+7 0 1.1 E+7 0 1.1 E-8 0 1.0 E.8 0 1.3 E+8 0 9.6 E+7 l Ce - 144 '
E+'1 0 '. 0 E.* 2 0 4.3 E+11 0 2.? E+11 & .-
lI - 1 31 1.7 I+9 0 i.9 E-3
.I - 133 0 9.6 I-9 0 3.9 E-9 0 8.5 E46 0 3.7 E46 0 2.2 E46 I - 135 0 2.0 E+7 0 ideritified 0 1.0 E+11 0 9 3 E+10 0 5.5 E+10 0 3 9 E+10
- mrev'yr **8
. rw./yr uCi/c pCi/sec 2 41 Rev. 8 7-1-82
TABLE 2-14 PARME'lIRS WED E CAlfULA1E Rg Paraneter Residere Beach Cenp Store Vegetable Meet Milk V., 2.0 (default) 2.0 2.0 2.0 2.0 2.0 W 2.0 (default) 2.0 2.0 2.0 2.0 2.0 YP 0.7 (default) 0.7 0.7 0.7 0.7 0.7 YC 2.0 (default) 2.0 2.0 2.0 2.0 2.0 QC 50 (default) 50 50 50 50 50 03 6 (default) 6 6 6 6 6 H 8.0 (default) 8.0 8.0 8.0 8.0 8.0 7 1.00 .05914 .228 .25 0.05 0 ZIN 1.00 .059ti .228 .25 0.05 0 FV 1.00 0 0 1.00 0 0 FP O O O O O 1.00 FU 0.76 0 0 0.76 0 0 FTF 0 0 0 0 0 1.00 FUT 0 0 0 0 0 0 FTG 0 0 0 0 0 0 FB 0 0 0 0 1.00 0 FBF 0 0 0 0 1.00 0 ff3IE: Pa aneters defined a) Page M of NURETA133 i
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l 2-42 gev. g 7-1-82
3.0 PROJECTED DOSES 3.1 Liquid Dose Projection (3.11.1.3)
The methodology used for projecting a liquid dose for specification 3 11.1.3 is as follows:
l I
l
- 1. Determine the average monthly total body and organ dose resulting from releases during release for the previous twelve months.
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l
! 2. Use the average monthly total body organ doses to make the dose projections.
3.2 Gaseous Data Projection (3 11.2.4)
The metnodology used for projecting a gaseous dose for
(
specification 3.11.2.4 is as follows:
- 1. Determine the average monthly total body and organ dose resulting from releases during the previous twelve months.
- 2. 'Jse the average monthly total tody and Organ dose to make the f dose projection.
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24 . 0 OPER ABILITY OF E3]IPMENT The flow diagrams defining the treatment paths and the components of the radioactive liquid, gaseous and solid waste management systems are shown in Figures 41 thru b3
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t 5.0 RADIOLOGICAL ENVIRONMENTAL MONITORING
- The Radiological Environmental Monitoring Sample Locations are identified in Figure 5-1. These sample locations are described in Tables 5-1 and 5-2 and indicates the distance in miles and the direction, determined from degrees true north, from the center of the Units 283 building complex. Table 5-3 gives the sector and direction designation for the Radiological Environmental Monitoring Sample Location Map, Figure 5-1.
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- If a milk producing dairy animal is discovered within the 5 mile radius of the Emergency Planning Zone (EPZ) during the annual land use census, a monthly sampling analysis of the milk will commence.
5-1 Rev. 8 7/1/82
Page 1 of 6 IABLE 5-1 RADIOLOGICAL ENVIRONMENTAL MONITORING SAMPLE LOCATIONS Distance
- Type of Sample and Sampling Location (Miles) Direction
- Direct Radiation 59 SONGS Meteorological Tower 0.3 NW 10 Bluff 0.8 NW 40 SCE Training Center - Japanese Mesa 0. 8 NW 8 Noncommissioned Officers Beach Club 1.2 NW 34 San Onofre School 1.7 NW 9 Basilone Road /1-5 Freeway Offramp 2.0 NW 21 Concordia Elementary Schcol - San Clemente 3. 5 NW 20 San Clemente Pier 5.0 NW 1 City of San Clemente (SD35E Offices) 5. 6 NW 24 San Clemente Hi;- 5:100' 5.0 NW 25 Convalescent Home - San ~.lererte 8.0 NW 23 San Clemente General Hospital 8.2 NW 26 Doheny Fire Station - Capistrano Beach 9. 5 NW 27 U.S. Post Of fice - Dana Point 10.5 NW 29 San Juan Capistrano Fire Station 10.8 NW 26 Dano Hills 4 ;- Sc o:1 11.3 '?W 27 Laguna Niguel Fire Station 13.5 NW 30 Laguna Beach Fire Station 17.5 NW 32 Santa Ana Police De;artme .t 32.0 NW
- Dista te (-iles i e-c : rect :a 'tecto-! are measured re'at ' .e to 'Jnits 233 n : point. D; recti.s is ::te ' e: from ce;rees true nortn.
5-2 Rev. 8 7/1/82
Page 2 of 6 TABLE 5-1 (Cont.)
RADIOLOGICAL ENVIRONMEr TAL MONITOPING SAMPLE LOCATIONS Distance
- Type of Sample and Sampling Location (Miles) Direction
- 14 Huntington Beacn Generating Station 37 NW.
39 Basilone Road Trailer Park 1.4 NNW 19 San Clemente Highlands 5.0 NNW 31 Aurora Park Mission Viejo 18.6 NNW 2 Camp San Mateo 3.5 N 33 Camp Talega 5. 7 N 11 Visitors Center 0.2 NNE 35 Range 312 (Marine Corps Base, Can; Pencleton) 4. 7 NNE 12 South Edge of Switchyard 0.2 NE 3 Camp San Onofre 2. 6 NE
, 36 Range 20BC (Ma-ine Corps Base, Ca p Pe-ci e :-) 4. 0 NE 41 Old Roate 101 - East 0.3 E 16 East Site Boundary 0. 5 E 4 Camp Horno 4.5 E 42 Horno Canyon 4.6 E 44 Fallbrook Fire Station 18.0 E
". 3 E5E Site sc.*:& j 0.2 E5E 7 Old Route 101 - ESE 0.5 ESE I
I 45 Interstate 5 Weigh Station 2. 0 ESE 6 Old Route 101 - ESE 3.0 ESE i
- Di stance (mile ' i c 01 re:: 4:n ',sectcr) a e measured reieti ve to 'Jnits 253 midpoint. Directi:r. is deter mi .ec f r om cegrees true r. orth.
I Rev. 8 l 5-3 l 7/1/82
Page 3 of 6 TABLE 5-1 (Cont.)
RAD 10;0GiCAL ENVIRONMENTAL MONITORING SAMPLE LOCATIONS Distance
- Type of Sample and Sampling Location (Miles) Direction
- 5 Camp Las Pulgas 8.5 ESE 49 Camp Chappo 12.8 ESE 4
48 Mainside (Marine Corps Base, Camp Pendleton) 15.0 ESE 52 Vista Fire Station 21 ESE 54 Escondido Fire Station 32 ESE 13 Site Boundary 0.13 SE 46 San Onofre State Beach Park 1.4 SE 38 San Onofre State Beach Park 3.6 SE 47 Camp Las Flores 8.6 SE 43 Edson Range (Marine Corps Base, Camp Pendleton) 10.6 SE 50 Oceansice rire Station 15.5 SE 51 Ca rls ba: Fire Station 18.6 SE 53 San Diego Coanty Operations Center 45 SE i 58 San Onofre State Beach (Unit 3) 0.1 5 57 San Onofre State Beach (Unit 2) 0.1 SSW 56 San Onofre State Beach (Unit 1) 0.1 W E5 Sar Orc' e 1;tte Seacn (Jr.it 1) 0.2 W 22 Coast Gsaro Station - San Mateo Point 2. 7 WNW 17 Transit Dose - -
1B Transit Dose - -
Distance (- les
- a : cirection (sector) are reasured relat ,e to 'Jrits 253 mi e; ai r,t. D' re:t' y is deterni nea f r or, ae;rees true nortr..
Rev. 8 5-4 7/1/82
Page 4 of 6 T ABLE 5-1 (Cont. )
RADIOLOGICAL ENVIRONMENTAL MJNITORING SAMPLE LO:1.!:JNS Distance
- Type of Sample and Sampling Location (Miles ) Direction
- Airborne 6 SONGS Meteorological Tower 0. 3 NW 1 City of San Clemente (SDG&E Offices) 5.5 NW 3 Huntington Beach Generating Station 37 NW 4 Northeast Site Boundary 0.2 NNE 2 Camp San Onofre 1. 8 NE 5 Units 283 Switchyard 0.13 ESE Soil Samples 3 basilore 003 '!-5 Free ay Of f ramp 2. 0 NW 4 Hantington Beach Generating Station 37 NW 5 East Site Boundary 0.2 NNW 1 Camp San Onofre 2.5 NE 2 Old Route 101 - SE 3. 0 SE Ccean nater &
D Newport Beach 3r NW A Station Discharge Outfall - Unit 1 0.5 SW B Datfall - Unit 2 0. 7 SW C O a t ' a ' l - L+. i t 3 0.7 SW
- Distance (miles) and direction (sector) are measured relative to Units 2&3 midpoint. Direction is determined from degrees true nortt.
Rev. 8 o susues
Page 5 of 6 TABLE 5-1 (Cont.)
R A.)l0t031C AL ENVIRONMENT AL MONITORING SAM?LE LOC A' IONS Distance
- Type of Sample and Sampling Location (Miles ) Di recti on*
Drinking Water j
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1 Tri-Cities Monicipal Water District 8. 7 NW Reservoir 3 Huntington Beach 37 NW 2 San Clemente Golf Course Well 3.5 NNW F
Sediment from Shoreline (Beach Sand) g 2 San Onofre Svfing Beach 0. 9 Nd 4 Newport Beach (North End) 30 NW l San Oncf e State Beach 0.6 SE 3 San Dr.c' e 1:a:e Sea:q 3.5 SE Local Crops 1 San Mates Ca.j:n 2. 6 NW 2 Southeas: Of '. :e a .si ce 22 SE 1
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Diste-:e # 'es a: cirecuc- (se:tcr) are eas.re: re'eti .e to L' it s 253 P* dpint. ;~ 'e::';" 15 ceter: - ed f roc cEgr-es *r oe ':,"tn.
l Rev. 8 5-6 7/1/82
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Page 6 of 6 l TABLE 5-1 (Cont.)
RAD 10dGICAL ENtlRONMENTAL MJNITORING SAMPLE LOCAT:0NS l Distance
- Type of Sample and Sampling Location (Miles ) Direction
- Non-Migratory Marine Animals $
C Newport Beach 30 Nd B Units 283 Outfall 0.7 SSW A Unit 1 Outfall 0. 6 WSW Kelp D Newport Bea:n 30 NW C Barn Kelp Bec 6.6 'SSE A San Onofre Kelp Bed 1.5 S B San Ma*.e: Ke': sed 3.5 WNW Ocean Bottor. Seciments h
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E Newport Bea:n 30 NW D Unit 3 Out'all 0.9 5 C L'n i t 2 ...'S 0. 8 554 l A Unit 1 Ostfali 0.5 W B Unit 1 Outfall 0.6 W 2 Jack Re:M 0.6 K4 1 Jea. Ra:1 g 0. L E
- Distance (miles) and direction (sector) are measured relative to Units 2&3 l mi$oint. Direction is determined f rom degrees true nortn.
5-7 g8 R
ABLE 5-2 RADIOLOGICAL ENVIRONMENTAL MONITORING SAMPLE LOCAT!DNS Di stance
- Pressurized len Chambers (Miles ) Di rection/Secto r*
(S1') San Onofre Beach -W - 0. 4 0 ~ ~ - - W P
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'52,s Visitors Center - NW 0.35 NW Q IS 3',' Japanese Mesa - NNW U.44 NNW R s.
'S4's MCB - Camp Pendleton -N 0.44 N A
($5' MCB - Camp Pendleton - NNE 0.41 NNE B 0.36 NE C IS6) MCB - Ca v Pendleton - NE
', S 7', MCB - Camp Pendleton - ENE 0.35 ENE D
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,- MCB - Camp Pendleton -E 0.44 E E
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IS9S San 0nofre State Beach - ESE 0.39 ESE F s ._ -
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- D1stence (-t ies; and direction 'se::o-) are .eass ed relatie :c cnits 213 nic;cir.t. D; ec ::n is deter-ice: f* n cegrees tese nar:..
Rev. 8 5-8 7/1/82
TABLE 5-3 SECTOR AND DIRECTION DESIGNATION FOR RADIOLOGICAL ENVIRONMENTAL MONITORING SAMPLE LOCATION MAP Degrees True North
\ from SONGS 283 Mid-Point Nomenclature Sector Center Sector 22.5u Limi t Line Limit Sector
- Direction 0 & 360 11.25 A N 348.75 33.75 B NNE 11.25 22.5 45 56.25 C NE 33.75 56.25 67.5 78.75 0 ENE 101.25 E E 78.75 90 101.25 112 123.75 F tsE 123,75 135 146.25 G SE 168.75 H SSE 146.25 157 168.75 ISO 191.25 J S 202.5 213.75 K SSW 191.25 236.25 L Sd 213.75 225 235.25 247.5 258.75 M WSW 281.25 N SW 258.75 270 w NW 281.25 292.5 303.75 P 326.25 S4 303.75 315 Q 337.5 348.75 R NNW 326.25
- The letters I and 0 have been omitted from these sector designators so as to j
i eliminate possible confusion between nombers and letters.
Rev. 8 5-9 7/1/82 1
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